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Bird Club
Bulletin of the African Bird Club Vol 17 No 2 September 2010
The perilious
conservation of the
montane forests of
northern Mozambique
Importance of
Aloe marlothii for
opportunistic avian
nectarivores
Investigating Lesser
Flamingo movements
using satellite-telemetry
Slender-billed Curlew
in Africa
A new subspecies
of Rock Firefinch in
north-east Nigeria?
Streaky-breasted
Flufftail in Benin
First record of
Chilean Skua in the
African region
Birding Rwanda in
search of Albertine
Rift endemics
ISSN 1 352-481 XISSN 1352-481X
^ fifrican Bird Club
The African Bird Club aims to:
• provide a worldwide focus for African ornithology
• encourage an interest in the conservation of the
birds of the region
• liaise with and promote the work of existing region-
al societies
• publish a twice-yearly colour bulletin
• encourage observers to visit lesser known areas of
the region
• encourage observers to actively search for globally
threatened and near-threatened species
• run the ABC Conservation Programme
Registered Charity No 1053920
ABC Membership
Membership is open to all. Annual subscription rates are:
Individual Europe & Africa: UK£1 8 Rest of the World: UK£20
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Supporting UK£30 minimum
Life UK£350
To join or for further details please visit the ABC website (where
there are secure online payment facilities) or write to the Membership
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ABC Website
http://www.africanbirdclub.org
Referees for Bull. ABC Vol. 17
John Ash, John Atkins, Phil Atkinson, Nicola Baccetti, Bas van
Balen, Ruben Barone, Nik Borrow, Stephan Brehme, Patrick Claffey,
Ron Demey, Harvey van Diek, Robert J. Dowsett, Franchise Dowsett-
Lemaire, Derek Engelbrecht, Lincoln Fishpool, Hilary Fry, Cees
Hazevoet, Guy Kirwan, Peter Lack, Olivier Langrand, Jeremy Lindsell,
Michel Louette, Graham McCulloch, Martim Melo, Michael Mills,
Bob Payne, Nigel Redman, Roger Safford, Jean-Marc Thiollay,
Steph Tyler
ABC Council
Phil Atkinson, Keith Betton (Chairman), John Caddick (Vice-
Chairman), Stephen Cameron, Clive Dickson, Chris Magin, Nigel
Redman, Danae Sheehan, Sue Walsh (Secretary) and Alan Williams
(Treasurer)
President: Tasso Leventis
Vice President: Martin Woodcock
Bulletin Editorial Board
Chairman of the Board: Keith Betton
Managing Editor: Guy Kirwan
Assistant Editor: Ron Demey
David Allan, Chris Bowden, Callan Cohen, Lincoln Fishpool, Peter
Lack, Pete Leonard (Graphics Editor), Jeremy Lindsell, Nigel Redman
and Steph Tyler
Contact ABC
African Bird Club, c/o BirdLife International, Wellbrook Court,
Girton Road, Cambridge CB3 ONA. E-mail: • info@africanbirdclub.
org • website: http://www.africanbirdclub.org
Further information can be obtained directly from individual
Council members by writing to them at the Club’s postal address, or
by e-mail as follows:
Chairman Keith Betton • chairman@africanbirdclub.org
Secretary Sue Walsh • secretary@africanbirdclub.org
Treasurer Alan Williams • treasurer@africanbirdclub.org
Bulletin Editor Guy Kirwan • editor@africanbirdclub.org
Conservation Officer Chris Magin
• conservation@africanbirdclub.org
Information Officer Keith Betton • info@africanbirdclub.org
Membership Secretary Danae Sheehan
• membership@africanbirdclub.org
Representatives Coordinator Clive Dickson
• reps@africanbirdclub.org
Corporate Sponsors Officer Stephen Cameron
• corporatesponsors@africanbirdclub.org
Photographers and artists
ABC is always looking for drawings and photos to publish in the
Bulletin. If you are interested in contributing, please contact the
Graphics Editor, Pete Leonard, pleonard@care4free.net
ABC particularly wishes to thank its Corporate Sponsors for their invaluable financial support in 2010: Abacus African Safaris, Ashanti
African Tours, Access Africa Safaris, Aim 4 Africa, Bens Ecological Safaris, Bird Feeding Station, Birdfinders, Birding Africa, Birding
and beyond Safaris, Birding Ecotours, Birdquest, Birdwatching Breaks, Calluna Books, Close Encounters, Crystal Safaris, Field Guides,
Greentours, Hyde-Lascelles, Lake Kitandara Tours and Travel, Lawson’s Birdwatching Tours, Limosa Holidays, MKA Ecology, Naturetrek,
Ornitholidays, Rockjumper, Sarus Bird Tours, Sunbird, Turaco Tours, Turtle Bay Beach Club, WildSounds, Wildwings, and Zeiss.
The Bulletin of the African Bird Club
The Bulletin of the ABC provides a forum for news, letters,
notices, recent publications, expedition results, reviews and
interim publication of studies on African birds by contribu-
tors from throughout the world. Publication of results in the
Bulletin of the ABC does not preclude publication of final
results as journal papers either by the ABC or elsewhere. No
material should, however, be submitted simultaneously to the
Bulletin of the ABC and to any other publication.
Brief notes for contributors appear elsewhere in this Bulletin
and further details are available from the Editor (editor@
africanbirdclub.org).
©2010 Copyright African Bird Club and contributors. Quotations should carry a full acknowledgement. No part etc may be
reproduced, copied or stored in a retrieval system without the prior written permission of the Club or authors.
Contents
Bull ABC Vol 17 No 2
News & Comment
Features
146
Club News
Compiled by Alan Williams
159
148
Conservation Fund News
151
Africa Round-up
Compiled by Ron Demey, Guy
178
M. Kirwan and Peter Lack
188
158
Advertising information
220
Photospot: Observations
du Faucon concolore
Falco concolor dans les
environs d’Antananarivo,
198
Madagascar
Bruno Boedts
202
225
Photospot: A breeding
island for Lesser
Flamingos Phoeniconaias
minor at Kamfers Dam,
207
Kimberley, South Africa
Mark D. Anderson and Tania
A. Anderson
210
239
Recent Reports
Compiled by Ron Demey
212
253
Reviews
257
Letter to the Editor
213
272
Notes for Contributors
215
Photographs
Mark Anderson, Julian Bayliss, Peter
Berglin, Bruno Boedts, Nik Borrow,
Merilyn Browne, Hugh Buck, Artur
Bujanowicz, Rod Cassidy, Callan
Cohen, Frangoise Dowsett-Lemaire,
Lincoln Fishpool, Dick Forsman, Matteo
Gagliardone, Brayton Holt, Keith
Larson, Graham McCulloch, Johannes &
Sharon Merz, Pete Morris, Phil Palmer,
Richard F. Porter, Carlos Ribeiro, Adam
Riley, Beneharo Rodriguez, Peter Ryan,
Volker Salewski, Martin Stervander,
216
217
229
Kristian Svensson, Craig Symes, Jonathan
Timberlake, Ray Tipper, Chris Townend,
Albie Venter, Tim Wacher, Alan
Williams, Ian White, David Winter
Front cover plate
Lesser Flamingo Phoeniconaias minor
by Mark D. Anderson
Further ornithological exploration of Namuli and
Mabu Mountains (northern Mozambique), and the
urgent need to conserve their forests Frangoise Dowsett-Lemaire
The sweet option: the importance of Aloe marlothil for
opportunistic avian nectarivores Craig Symes
Investigating Lesser Flamingo Phoeniconaias minor
movements and the potential connectivity among
regional populations using satellite-telemetry Volker Salewski,
Brooks Childress and Martin Wikelski
Brief notes on the birds of Mount Inago,
northern Mozambique Lincoln D. C. Fishpool and Julian Bayliss
The Slender-billed Curlew Numenius tenuirostris in Africa
Graeme Buchanan, Nicola Crockford and Adam Gretton
Hybrid Eurasian Coot Fulica atra * Common Moorhen
Gallinula chloropus on Tenerife, Canary Islands
Beneharo Rodriguez, Juan Curbelo and Nazaret Carrasco
Rock Firefinch Lagonosticta sanguinodorsalis in the Mandara
Mountains, north-east Nigeria: a new subspecies?
Jacinta I. Abalaka, Ulf Ottosson, Talatu Tende and Keith Larson
A record of brood parasitism of Barratt’s Warbler Bradypterus
barratti by African Emerald Cuckoo Chrysococcyx cupreus
Michael S. L Mills
First record of Streaky-breasted Flufftail Sarothrura boehmi
for Benin Johannes Merz and Sharon Merz
First records of Ruddy Turnstone Arenaria interpres for Benin
Guy R. Manners
First record of Grey-necked Picathartes Picathartes oreas
for Central African Republic Rod Cassidy, Barry Watkins and
Tamar Cassidy
First record of Chilean Skua Catharacta chilensis for the
African region Peter G. Ryan
Birding Rwanda — in search of Red-collared Babbler
Kupeornis rufocinctus, Albertine Rift endemics and more
Callan Cohen, Peter Ryan, Marcell Claasen and Claver Ntoyinka
THE NATURAL
HISTORY MUSEUM
2 h AUG 2010
PURCHASED
TRING LIBRARY
Bull ABC Vol 17 No 2 (2010) -145
Club News
ABC 2010 Thetford meeting and
AGM
The Club held its annual meeting
and AGM on 10 April 2010 at
the British Trust for Ornithology’s
(BTO) headquarters in Thetford,
Norfolk. Chairman Keith Betton
welcomed all those who had come
to the meeting. He thanked the
BTO for once again making their
headquarters available for the venue
on what was a beautiful day. Keith
welcomed Kabelo Senyatso, Director
of BirdLife Botswana, to the meeting.
He drew attention to Martin
Woodcock’s new book, which was
available at the AGM. He thanked
WildSounds for their support and
also thanked Bev & Geoff Randall
for their work on the sales goods.
The programme of talks followed, on
interesting and varied subjects.
House Crows in Africa:
villain or victim ? — Colin Ryall
described the House Crow’s Corvus
splendens native range in the Indian
subcontinent. House Crows became
established and expanded in other
countries due to deliberate releases,
Figure 1. Speakers at the ABC annual
meeting, Thetford, April 2010, with
from left to right: John Caddick,
Colin Ryall, Glyn Young, Anthony
Cizek, Nigel Redman and John Gale
(Alan Williams)
Conferenciers a l’Assemblee generale
annuelie de l’ABC, Thetford, avril
2010 ; de gauche a droite : John
Caddick, Colin Ryall, Glyn Young,
Anthony Cizek, Nigel Redman et John
Gale (Alan Williams)
ship-assisted passage and overland
spread. They now occur through
much of coastal East Africa, and
even in Australia, Chile and the
Caribbean. Everywhere the species
is omnivorous, klepto-parasitic and
a carrion-eater. Aden, Zanzibar and
Suez were early strongholds and,
although mainly coastal, House
Crows have spread inland from
Dar-es-Salaam in Tanzania. They
reached Durban in 1972 but have
been eradicated from East London
and Port Elizabeth. Two eradication
programmes have been successful —
on Socotra and the Seychelles, and
real attempts at eradication are being
made in the Western Cape of South
Africa. He described their adverse
impacts on native avifauna, the
nuisance they cause and the damage
they inflict on crops and livestock.
His answer to his own question was
that House Crows are indeed villains.
He suggested anyone interested visit
www.housecrow.com or contact him
at colin.ryall@ntlworld.com.
ABC Conservation Tour to
Siena Leone. — John Caddick spoke
about the highlights of the ABC
Conservation Tour to Sierra Leone,
which took place in December 2009
and was organised by Rockjumper.
It followed the theme of previous
tours by giving members the
opportunity to visit some ol the less
well known and ornithologically
interesting parts of Africa while
simultaneously generating income for
the Conservation Fund. A full report
appeared in Bull. ABC 17: 3—4.
Bird conservation challenges
in Zimbabwe. — Anthony Cizek
began by describing the closure
of the Kariba dam and the species
rescue that ensued in the late 1950s.
I suspect that, like myself, many
older UK members will recall this
from the newsreels of the day.
Although bird conservation was
seen as a priority at all levels of
government during the changes
from Rhodesia to Zimbabwe, recent
events in the political development
of the country have resulted in the
population concentrating on survival
rather than wildlife preservation. By
highlighting the many and varied
habitats of ornithological interest in
Zimbabwe, Anthony demonstrated
the potential for loss of much that
should be preserved. However, there
was some optimism, and Anthony
highlighted the work that is being
done in many areas through the .
Communal Areas Management
Program for Indigenous Resources
initiative, which encourages local
peoples’ cultural instinct to conserve
natural resources. They share in the
income generated from the wildlife
parks. This endeavours to ensure that
wildlife and rural communities can
co-exist.
Saving the Madagascar
Pochard. — Glyn Young (Durrell
Wildlife Conservation Trust) gave a
detailed account of the ongoing work
to save one of the world’s rarest birds,
Madagascar Pochard Aythya innotata.
The pochard was feared extinct by
the late 1990s but in 2006 a group
from the Peregrine Fund observed
20-30 birds on a volcanic lake in
northern Madagascar (see Bull.
ABC 14: 171—174). This location
provided the fringing marsh the birds
require. Surveys in 2008—09 revealed
no addition to the population.
Given that the loss of young birds
would quickly lead to the duck
becoming extinct, the decision was
taken to establish a captive-breeding
programme. Glyn detailed how this
was done, which was quite a feat
given the condition of the roads and
the necessity ol getting the chicks
to a protective environment swiftly.
Having achieved this, much remains
to be done to preserve this Critically
Endangered species, particularly
identifying a good relocation site.
1 46 - Bull ABC Vol 17 No 2 (2010)
Club News
Morocco: land of contrasts. —
Nigel Redman showed us that good
birding is available in Morocco. It
is easily accessible to Europeans, has
Mediterranean and Atlantic coastlines
as well as deserts and mountains.
With a list of 450 species, 200 of
them regular breeders, there is plenty
of scope for exciting birding. There
are no true endemics, but Northern
Bald Ibis Geronticus eremita, Houbara
Bustard Chlamydotis undulata ,
Dupont’s Lark ChersophiLus dnponti,
Thick-billed Lark Ramphocoris
clotbey and Dark Chanting Goshawk
Meliarax metabates are enough to
tempt the well-travelled African
birder. Nigel took us to some of the
best sites such as Oued Massa near
Agadir and the Atlas Mountains.
The extreme south of Morocco is
less accessible than other parts of the
country, but it offers great potential
for birders in the future.
Bird illustrating in
Madagascar. — John Gale gave a
fascinating account of the work of
the bird artist. He took us through
the process of completing plates of
species from sketches in the field,
researching skins and available
photographs to the final product.
The layout of the plates is done
with meticulous precision and
many amendments are made before
achieving a satisficatory result.
Even finding the bird can be time
consuming as he took seven days
to locate Sunbird Asity Neodrepanis
coruscans , for his latest project, the
Handbook to the Birds of the Indian
Ocean Islands. Next time you pick
up a field guide, spare a thought
for all the hard work the artist has
put into the illustrations.
2010 AGM
ABC Council has decided not to
publish the Summary Accounts
and detailed report of the AGM
in Club News in order to allocate
more space for papers. The
information is available on the
Club website www.africanbirdclub.
org. A brief summary of the main
items follows.
Outgoing Treasurer John Caddick
reported that the Club had managed
to produce a surplus of income over
expenditure of UK£5,500 and had
made Conservation Fund awards
of over UK£10,000 in 2009. John
is now standing down as Treasurer
after a period of seven years. He
will continue on Council as Vice-
Chairman and will be concentrating
on the Club’s website in the
future. Alan Williams, currently
Membership Officer, is taking over
as Treasurer. Alan was also Treasurer
in 1998-2002. Steph Tyler has
completed her term as Conservation
Officer. Many of you will know
Steph, and her knowledge of African
ornithology has been put to good use
in the handling of applications for
Conservation Fund grants in many
countries. In the seven years she
has been in situ , the Club has made
over UK£62,000 of grants. This in
itself is testimony to the amount of
effort Steph and the other members
of the Conservation Committee
have put in. Chris Magin has taken
over as Conservation Officer. Since
completing his Ph.D. in Tanzania,
Chris has worked as a conservationist
for over 20 years, for a variety of
conservation organisations in many
different countries, principally in
Africa. He is currently International
Officer for Africa for the Royal
Society for the Protection of Birds
(RSPB), but previously worked for
BirdLife International in Morocco,
WWF in Niger, IUCN in Djibouti
and several organisations in Kenya.
He has advised on expedition /
research applications for Raleigh
International, Rufiford Small Grants
and for several years managed
the RSPB’s Africa Small Grants
Programme.
Three new Council members
were appointed. Danae Sheehan is
the new Membership Officer. Danae
currently works for the International
Research Department of the
RSPB at Sandy as a Conservation
Scientist. She regularly visits
Africa. Stephen Cameron has been
elected as Corporate Sponsorship
Officer. Stephen is a retired hospital
physician, based in North Yorkshire,
who has visited 15 countries in Africa
on 30 occasions, and returns to the
continent most years. He took over
as Corporate Sponsorship Officer in
2009 as a co-opted Council member
and will now continue in this role as
a full Council member. Sue Walsh is
the new Secretary. Sue, who runs a
business called WorkLife Architect,
which works with people to help
them achieve their goals in life, has
travelled all over the world birding,
including to several countries in
Africa. She lives in Brighton and is
involved in Sussex birding as well as
the African Bird Club.
2011 AGM
The 201 1 AGM will be held
on Saturday 16 April 2011 at
Swedenborg House, 20-21
Bloomsbury Way, London WC1A
2TH. This announcement constitutes
official notification of the AGM as
required by the Club’s constitution.
Full details of the AGM agenda and
programme for the day will be posted
to all UK members at least one
month before the meeting. To save
postage, the programme will not be
automatically distributed to members
outside the UK. Any overseas
member wanting a copy, either by
post or e-mail, can write to the Club
Secretary. Details will also appear on
the Club website.
Club News
Bull ABC Vol 17 No 2 (2010) - 147
African Bird Club Conservation Fund
This will be my last report as Conservation Officer
for ABC after eight years at the helm. My term
of office on ABC Council ended at the AGM in
April and Chris Magin has since taken over. I
have greatly enjoyed being in contact with both
budding and more experienced ornithologists
throughout Africa.
Conservation Awards
Expedition Award: survey of vultures in
Sudan
The proposal submitted by Ivaylo Angelov,
for a study of the distribution, population and
limiting factors for migrant Egyptian Vultures
Neophron percnopterus on the Red Sea coast of
Sudan, received strong support from the ABC
Conservation Committee and Council. The
project will be implemented jointly by the
Bulgarian BirdLife partner and the Sudanese
Wildlife Society (SWS), the leading nature
conservation NGO in the country. Egyptian
Vulture was recently classified as Endangered
following a sharp long-term population decline.
In the Balkans the species probably will become
extinct in the next 20-25 years if the trend is
not reversed, and it is known that there are
heavy losses of birds during migration and
winter in Africa. The main threats in Africa are
Egyptian Vulture / Vautour percnoptere Neophron
percnopterus (Dick Forsman)
poisoning, electrocution and, in some countries,
probably shooting. Sudan is the largest country
in Africa and formerly supported high densities
of vultures, but all species including Egyptian
Vulture have dramatically declined. During
three brief visits to Port Sudan (in 1982-83
and 2005), German ornithologists recorded >60
electrocuted Egyptian Vultures below a single
10-km stretch of power line along the western
Red Sea coast, which suggests that this power
line alone could be playing a significant part in
the species’ decline. Although vulture experts
working throughout Africa have pointed out
that research into the conservation of all vulture
species, especially in the northern half of the
continent, is an urgent priority, to date almost
nothing has been done. The expedition will
aim to plan urgent conservation measures for
Egyptian Vultures along Sudan’s Red Sea coast.
Among the project’s objectives are to study
the threats to migrating vultures and to build
local capacity for future conservation of the
species by training Sudanese ornithologists in
this work. ABC thanks Olle Holst of Avifauna
for supporting this project.
Further work on Djibouti Francolin
ABC is most grateful to Julian Francis, who
has sponsored the award of UK£ 1,000 to
Houssein A. Rayaleh, Executive Secretary of
Djibouti Nature, to support his field work
costs during forthcoming work on Djibouti
Francolin Francolinus ochropectus. This award
was previously announced in Bull. ABC 17:
8-9.
Reconciling forest use and bird
conservation in south-west Madagascar
At the February Council meeting an award of
UKT756 to Charlie Gardner was approved. The
objectives of his project were to quantify the
impacts of forest use, e.g. charcoal production,
on bird community composition and structure,
and on vegetation composition and structure, as
well as to make recommendations to protected
area managers regarding forest use and bird
conservation. An interim report has already
been received. Aside from detailed bird surveys,
interviews have been undertaken with local
148 -Bull ABC Vol 17 No 2 (2010)
ABC Conservation Fund
^ African Bird Club Conservation Fund
villagers and a slide show is in preparation for use
in local villages to demonstrate the importance
of bird conservation.
Ecology and conservation status of
Aberdare Cisticola in Aberdares National
Park, Kenya
This project, which will be undertaken by
Philista Malaki of the National Museums of
Kenya, Ornithology Section, has been awarded
UKi.800. Aberdare Cisticola Cisticola aberdare
is listed as globally Endangered. The species
inhabits moist grassland in Mau Narok-Molo
and the Aberdares in central Kenya, and is
threatened by habitat loss due to agricultural
expansion. Frequent fires in Aberdare National
Park represent an additional threat. The specific
objectives of the research are as follows. To
estimate the population of Aberdare Cisticola in
the national park; to determine the species’ spatial
distribution and habitat selection; to evaluate the
current extent, quality and rate of loss of its
habitat; to identify and quantify specific threats;
to explore local attitudes to its conservation;
and to identify probable stakeholders in its
conservation.
Reports
Stripe-breasted Tit
Phil Shaw and Douglas Shell have sent a report
on their work on Stripe-breasted Tit Parus
Stripe-breasted Tit / Mesange a ventre strie Parus
fasciiventer (Kristian Svensson)
fasciiventer at Ruhija, Bwindi Impenetrable
National Park, in Uganda. The award, made in
2009, has enabled a much fuller investigation
of the species’ breeding ecology and survival
than would otherwise have been the case. The
data collected during 2009, combined with
the previous dataset, will enable a much better
understanding of the links between current
climate, leaf phenology and breeding activity in
this scarce Albertine Rift endemic.
Sam Osinubi
Samuel Temidayo Osinubi received an
ABC award that was kindly matched by our
President, Tasso Leventis. Sam attended a sound
analysis workshop at the Cornell Laboratory of
Ornithology, which provides a basic practical
understanding of spectrographic analysis along
with an introduction to the wide range of
techniques used in sound analysis and their
application in biological research. Sam’s doctoral
research aims to examine the influence of
habitat quality on several adaptive behaviours
of bird species resident in an Afromontane
forest in Nigeria. One of the behaviours studied
is vocalisation, relative to microhabitat and
individual fitness. Bioacoustics research is a
nascent area of indigenous ecological study in
Nigeria, if not Africa as a whole, making Sam’s
attendance at the workshop doubly important.
The opportunity arose for him to undertake a
‘crash course in sound data collection, working
with Macaulay Library staff. His analyses
focused on recordings of Yellow-breasted
Boubou Laniarius atroflavus made during the
first field season of this research. The use of
personal recordings for sound analyses during
the workshop permitted a better understanding
and appreciation relative to each participant’s
research needs.
North Nandi Forest
Simon Musila, Alex Syingi and Jackson Sajita
have reported on surveys undertaken in the
North Nandi (Kenya) Important Bird Area. In
the eastern part of the forest they found 108
species, of which 33 were forest specialists.
Unfortunately no globally threatened Chapin’s
Flycatchers Muscicapa lendu were found, but
ABC Conservation Fund
Bull ABC Vol 17 No 2 (2010) -149
^ African Bird Club Conservation Fund
the team did observe five Turner’s Eremomelas
Eremomela turneri. They also found that relatively
little habitat degradation had occurred in the
decade since the previous survey.
Steph Tyler, on behalf of the
Conservation Committee
The ABC website (www.africanbirdclub.org/
club/consfund_projects.html) shows the full list
of conservation projects and awards made since
the inception of the programme ten years ago.
A remarkable total in excess of UK£90,000 has
been donated during this period. You can also
view many of the final project reports on this
page.
Turner’s Eremomela / Eremomele de Turner Eremomela
turneri (Pete Morris)
Africa is just one
of the Continents
we offer
For the top
destinations
contact
Birdfmders
01258 839066
info@birdfinders.co.uk
www.birdfinders.co.uk
Stop wishing, start packing!
150 -Bull ABC Vol 17 No 2 (2010)
ABC Conservation Fund
General
One confirmed extinction but
some successes
BirdLife International has
announced, in the 2010 IUCN Red
List update for birds, the extinction
of Alaotra Grebe Tachybaptus
rufolavatus, although this might
come as little surprise to readers
of this Bulletin ( cf Bull. ABCl\
115-117). Restricted to a tiny area
of eastern Madagascar, the grebe
declined rapidly after carnivorous
fish were introduced to the lakes in
which it lived. This, along with the
use of nylon gill nets by fisherman
that caught and drowned birds, has
driven this species into the abyss.
“No hope now remains for this
species. It is another example of how
human actions can have unforeseen
consequences”, said Dr Leon
Bennun, BirdLife International’s
Director of Science, Policy and
Information. However, one ‘plus’
is that Azores Bullfinch Pyrrhula
murina has been downlisted from
Critically Endangered to Endangered
Azores Bullfinch / Bouvreuil des Aqores
Pyrrhula murina (Carlos Ribeiro)
as a result of conservation work to
restore natural vegetation on its
island. The Portuguese and UK
BirdLife partners have worked
together with others to transform the
fortunes of this species in what is a
model for other projects. “This is a
clear example of conservation action
succeeding in turning the tide for a
highly threatened species”, said Andy
Symes, BirdLife’s Global Species
Programme Officer. “Where there is
commitment and financing we can
save species. We have the knowledge
and will, but there needs to be better
funding globally to address the loss
of species. ”
Source: www.birdlife.org
Migrants use an intermittent
strategy in spring too
Recent evidence from radar studies
of Palearctic migrants crossing
the Sahara Desert in autumn
suggests that most passerines use an
‘intermittent strategy’. In autumn
migrants with quite high fuel loads
have been found to rest in the desert
by day and to fly during the night,
whereas lean individuals are often
found to rest in oases for several
days to refuel. Now a spring study
by Volker Salewski and others of
Vogelwarte Radolfzell working in
the plain desert of Mauritania have
found that most birds captured
had fat loads sufficient to reach
the northern edge of the desert
with a similar intermittent strategy.
Furthermore, birds in a nearby oasis
did not carry consistently lower fuel
loads than those caught in the desert
itself. In other words, birds found on
the ground in spring in the Sahara
do not represent falls, but are birds
simply resting and quite capable of
completing their journeys.
Source: J. Ornithol. 151: 371— 378
Biodiversity in Africa’s protected
areas declining fast
BirdLife International is working
in 22 countries in Africa and in
over 1,200 IBAs. While all of these
countries have increased their efforts
to conserve biodiversity, much more
remains to be done. A monitoring
project of protected areas (covering
1 17 sites in seven countries)
implemented by BirdLife and the
Royal Society of the Protection of
Birds (BirdLife in the UK) clearly
shows that the state of biodiversity
is declining. Sites identified as being
in a poor state increased from 43%
in 2001, to 57% in 2008. At the
same time there has been a general
increase of threats facing protected
areas. However, “The results also
show that if proper management
responses are put in place it is
possible to improve the state of
biodiversity and reduce pressures”,
said Achilles Byaruhanga (Executive
Director of Nature Uganda). “This
was well demonstrated through the
sites monitored in Botswana, Central
Kalahari Game reserve, Okavango
Delta and Mannyelanong, where
comprehensive and effective uses of
existing management plans have been
instituted”. Nonetheless, it is clear
that urgent action will be needed
to halt biodiversity loss and prevent
extinctions, while simultaneously
contributing to human well being
and poverty reduction.
Source: BirdLife International press
release, May 2010
Update on the Amur Falcons . . .
In the last Bulletin {Bull. ABC 17:
1 1—12) we reported on the first
stage of a project to develop a better
understanding of the incredible
migration of the Amur Falcon Falco
amurensis, which breeds in north-
east Asia and principally winters
in southern Africa. Over the last
decade, satellite telemetry has been
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Bull ABC Vol 17 No 2 (2010) -151
Amur Falcon / Faucon de l’Amour
Falco amurensis (Adam Riley)
successfully used to understand the
migrations of many Eurasian raptors
that winter in Africa, and now this
technique is being used with Amur
Falcons. By 9 May 2010, the first
bird had reached eastern China,
having covered c. 13,750 km in seven
weeks, sometimes in ‘leaps’ of >1,000
km in a single day. A second bird
reached the same area three days
later. Remarkably, one male was still
in Somalia, near Mogadishu, at the
same time.
Source: Bernd Meyburg in litt. to
African Birding May 2010
. . . and stable isotopes also
assist
Stable isotopes have been measured
in adult and juvenile Amur Falcon
Falco amurensis feathers in a further
bid to understand the migratory
connectivity of this species. The
data suggest that juvenile Amur
Falcons in South Africa originate
from across their entire Palearctic
range, but roost site fidelity is low
in the overwintering range, where
the birds move widely, feeding on
a broad range of arthropods that
are seasonally abundant. Total
population estimates for South Africa
are significantly lower than global
estimates meaning that a significant
proportion of the population may
not winter in South Africa or that
the global population is substantially
lower than believed. While roosts
can number hundreds to thousands
and are often in large exotic trees,
habitat changes particularly due to
agriculture, forestation and strip
mining, may affect the species’
numbers in the winter quarters.
Source: Bird Conserv. Intern.
doi:10. 1017/S09592709 10000237
North Africa
First record of Lesser Flamingo
for Algeria
On 31 December 2009, a Lesser
Flamingo Phoeniconaias minor was
photographed among a group of 900
Greater Flamingos Phoenicopterus
roseus at Lake Fetzara, in north-east
Algeria. This appears to be the first
record of this species for the country.
There are several previous records
from Morocco, but none from
Tunisia.
Source: Alauda 78, p. 26
Breeding of Greater Flamingo in
Algeria, 2003-09
Previously considered to be only
a winter visitor to the country,
since 2003 Greater Flamingos
Phoenicopterus roseus have bred
regularly at three different sites
within the Sebkha Ezzemoul, on the
Hauts Plateaux, in north-east Algeria.
A total of four of those breeding
attempts have proven successful,
with a total of >15,000 chicks
fledging, but other efforts have been
prejudiced by human disturbance
and to some extent drought.
Source: Alauda 78, pp. 15—25
On the reported Humblot’s Fleron
in Tunisia
The report of a ‘Humblot’s
Heron’ Ardea humbloti, which was
photographed at Oued Gouifla,
southern Tunisia, on 17 October
2008 (see Bull. ABC 17: 12),
was examined by Frederic Jiguet,
who, after careful study of the
photographs, concludes that the bird
in question was in fact a Grey Heron
A. cinerea with soiled or melanistic
plumage. Humblot’s Heron is a rare
endemic to the Malagasy region
and its occurrence in Tunisia was
extremely unlikely.
Source: Alauda 78, p. 40
Gull-billed Tern / Sterne hansel
Sterna nilotica (Peter Berglin)
Data on colonies of three tern
species at Sfax, Tunisia, 2004-06
In a recent paper, M. A. Chokri and
co-workers present data on three
tern species breeding in numbers
of both national and international
importance at the 1,600-ha salt
works near Sfax, in central-east
Tunisia. In the three study years,
2004-06, Gull-billed Tern Sterna
nilotica numbered 144-249 pairs,
Common Tern S. hirundo 321—625
pairs and Little Tern S. albifrons
194-272 pairs. Egg laying started
from late April to late May in Gull-
billed Tern (clutch size 1-3), and in
the third to fourth week of April in
Common and Little Terns (clutch
size 1-4). The number of fledged
juveniles per pair was highly variable:
0.0-0. 8 for Gull-billed Tern, 0-2
for Common Tern and 0.0-1. 8 for
Little Tern. This low reproductive
success is thought to be mainly due
to terrestrial predation, especially by
stray dogs, and disturbance.
Source: Alauda 78, pp. 51-60
African Reed Warbler discovered
in Libya
African Reed Warbler Acrocephalus
baeticatus, previously known only
from sub-Saharan Africa, was
discovered breeding in Benghazi,
Libya, in May 2008. Several
individuals were trapped and
subsequent DNA analysis confirmed
their identification. Further searches
produced another record of breeding
African Reed Warblers in the Libyan
desert, some 930 km from the
nearest isolated breeding area of A.
b. cinnamomeus in north-east Niger.
Surprisingly, reed warblers trapped
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Africa Round-up
in eastern Libya and western Egypt
proved to be close to ‘Mangrove Reed
Warbler’ A. scirpaceus avicenniae ,
known from southern Red Sea coasts.
Eurasian Reed Warblers A. scirpaceus,
presumably on passage, were also
caught and observed. The situation
of reed warblers in North Africa is
therefore complex. It was previously
assumed that reed warblers occurring
in reedbeds from Morocco to Libya
were A. scirpaceus. The present
records of African Reed Warbler in
Libya now beg the question whether
this taxon has been overlooked in the
other Maghreb countries. Further
studies are clearly needed to elucidate
the status and distribution of all of
the taxa involved.
Sources: Limicola 23, pp. 202-232 &
Birding World 23, pp. 218-219
Egyptian records
A recent paper by Jean-Philippe
Siblet reports records of 30 species
in Egypt, based on two visits to the
country, in July / August 2008 and
March 2009. Many of the records
pertain to the distribution of herons,
among them a total of six individuals
at three sites (and on two separate
dates) along the River Nile of a
species not previously recorded in the
country, Intermediate Egret Egretta
intermedia. As this species is easily
misidentified, it seems remarkable
that the author makes no effort to
validate or document his sightings
(and that the editors did not insist on
this), by including a description of
the birds involved.
Source: Alauda 78, pp. 69-73
Reintroduction of Sacred Ibis in
Egypt planned
Sacred Ibis Threskiornis aethiopicus,
which was abundant during the
dynastic period of ancient Egypt,
became extinct in the country in the
19th century. Nature Conservation
Egypt (BirdLife in Egypt) and
the Ligue pour la Protection des
Oiseaux (BirdLife in France) are
now planning to reintroduce the
species. There is a sizeable population
breeding wild in France, established
over recent decades by escapees
from zoos. The plan is to transfer
some of these birds to Egypt in a
Sacred Ibis / Ibis sacre Threskiornis
aethiopicus (Ian White)
controlled experiment and see if they
adapt to suitable habitat. A steering
committee composed of scientists
and veterinarians is studying all
aspects of the proposal.
Source: BirdLife Africa Newsletter
12(1), p. 11
Three-banded Plover breeding in
Egypt
Following the first record in 1993,
there has been a regular series of
sightings of Three-banded Plover
Charadrius tricollaris in the vicinity
of Aswan, in the far south of Egypt,
since early 2006. These culminated
in the confirmation, in April 2009,
that the species was breeding there,
providing the first evidence of nesting
in the Western Palearctic.
Source: Dutch Birding 32,
pp. 126-128
African Palm Swift in North Africa
Pierre-Andre Crochet and Marcel
Haas have recently re-evaluated
the status of African Palm Swift
Cypsiurus parvus in the Western
Palearctic, from where there are
records in Egypt and Mauritania.
The authors conclude that neither
of the mentions in the literature
for the first-named country can be
accepted for varying reasons (one
actually pertains to modern-day
Sudan), but (apparently reluctantly)
accept that the species’ presence on
the Western Palearctic list can be
maintained on the basis of a single
sighting from northern Mauritania,
albeit lacking documentation. It
seems that enterprising birders in this
part of Africa should be watchful for
the opportunity to make the species’
presence on this list more indelible.
Source: Dutch Birding 32, pp.
131-132
Identification of Atlas Flycatcher
A well-illustrated article published in
a recent issue of Dutch Birding deals
with the summer identification of
Atlas Flycatcher Ficedula ( hypoleuca )
speculigera, which has recently
been recommended to constitute a
species apart from Pied Flycatcher
F. hypoleuca. The paper attempts
to consolidate the features (and
variation) useful for separating adult
males, in particular, but also adult
females, especially with respect to the
very similar F. h. iberiae. The latter
taxon breeds in Iberia, but also passes
through North Africa on migration.
Source: Dutch Birding 32, pp.
155-162
West & Central Africa
Bird list of Gola Forest, Sierra
Leone, updated
Recent surveys have updated the total
number of bird species recorded in
Gola Forest and on neighbouring
Tiwai Island, Sierra Leone, to 327, of
which 313 have been found in Gola
and 176 on Tiwai. These have been
documented in a paper by Erik Klop,
Jeremy Lindsell and Alhaji Siaka. All
species of global concern previously
found in Gola were encountered,
including significant numbers of
White-breasted Guineafowl Agelastes
meleagrides and White-necked
Picathartes Picathartes gymnocephalus,
as well as small numbers of Rufous
Fishing Owl Scotopelia ussheri ,
Western Wattled Cuckooshrike
Lobotos lobatus, Nimba Flycatcher
Melaenornis annamarulae and Gola
Malimbe Malimbus ballmanni.
Source: Malimbus 32, pp. 33—58
. . . and avifauna of Bui National
Park, Ghana, documented
Bui National Park, in western Ghana
at the border with Cote d’Ivoire,
covers c. 1,821 km: and is crossed
by the Black Volta River. In 2008,
work started on a hydroelectric
power station and dam at Bui Gorge
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Bull ABC Vol 17 No 2 (2010) -153
immediately south of the park.
All land below r. 1 80 m eventually
will be flooded, including the
southern two-thirds of the riparian
forest, forested islands and adjacent
woodland. A unique community, at
the northern limit of the Guineo-
Congolian/Sudanian transition zone
will be destroyed. Bob Dowsett and
Fran5oise Dowsett-Lemaire spent
nearly ten days in Bui, in March
2005, and recorded 227 species,
among them several that are poorly
known in Ghana, e.g. White-backed
Night Heron Gorsachius leuconotus,
Pel’s Fishing Owl Scotopelia peli,
African Barred Owlet Glaucidium
capense, Dorst’s Cisticola Cisticola
guinea , Puvel’s Illadopsis Illadopsis
puveli and Yellow-billed Oxpecker
Buphagus africanus. Although the
list cannot be considered complete,
the Dowsetts place it on record in
view of the forthcoming habitat
destruction.
Source: Malimbus 32, pp. 1-21
Large shipment of African Grey
Parrots seized
More than 1,000 illegally trapped
African Grey Parrots Psittacus
erithacus en route to the Middle
East were confiscated at Douala
airport in early February 2010.
This is the largest group ever seized
in Cameroon and the third such
confiscation of the species in the
country since December 2007.
Some 300 birds were seized in
November 2009 alone. The parrots
were taken to the Limbe Wildlife
Centre, where 47 were found to be
already dead, with another 30 dying
of thirst and stress the following
day. Limbe Wildlife Centre and the
Last Great Ape Organization, two
independent African wildlife rescue
groups, are working with government
officials to co-ordinate the seizures
and subsequent care of the birds
in an attempt to reduce the trade
in African Grey Parrot, which is
classified as Near Threatened.
Source: www.ivildlifeextra.com
Mount Cameroon declared a
National Park
In response to the severe threats
posed by the growing human
population, in December 2009 the
Cameroon government decreed that
Mt. Cameroon and the surrounding
area would be designated a national
park. The new park is 58,178 ha
in extent and is an Important Bird
Area, with some 370 bird species
recorded to date, including most of
Cameroon’s montane endemics. Two
of the latter are known only from
Mt. Cameroon: Mount Cameroon
Francolin Francolinus camerunensis
(Endangered) and Mount Cameroon
Speirops Speirops melanocephalus
(Vulnerable). The site is also the
only known Cameroon locality for
Mountain Saw-wing Psalidoprocne
fuliginosa. It is hoped that the new
national park status will both protect
the unique ecosystem and bring
economic benefits to the human
inhabitants.
Source: wwf.panda.org
Entire Lake Chad finally
designated a Ramsar site
Following Niger, Chad and Nigeria,
Cameroon has designated its 12,500-
ha of Lake Chad as a Ramsar site,
effective on World Wetlands Day, 2
February 2010, thus completing the
Ramsar coverage of Africa’s fourth
largest lake. This will make the lake
the largest of the formally recognised
transboundary wetlands in the world,
and only the second in Africa. Lake
Chad is known to frequently support
over 200,000 birds, as well as various
threatened fauna and flora. The
vast populations of migrant birds
are sustained in part by midges,
the aquatic larval stage of which
(together with other zooplankton
and phytoplankton) are at the base
of the food chain of the abundant
fish population. Unfortunately,
the area is threatened by climate
change, desertification and poor
resource management.
Source: www.ramsar.org
Atlantic Ocean Islands
New journal
Zoologia Caboverdiana is a new
journal established by the Sociedade
Caboverdiana de Zoologia, which
body has set itself the goal of
promoting all manner of zoological
research within the Cape Verde
archipelago. The editor of the
journal is Kees Hazevoet, and
the first issue contained a major
paper on birds, the sixth update to
Hazevoet’s Cape Verde checklist.
Twenty-five new species for the
archipelago are reported therein,
among them vagrants from North
America (e.g. Baird’s Sandpiper
Calidris bairdii ), Europe (Eurasian
Wigeon Anas penelope), Africa
(African Crake Crex egregia ) and
the South Atlantic (Trindade Petrel
Pterodroma arminjoniana ). The
current situation of some endemic
taxa is also discussed, some of which
are Critically Endangered (e.g.
Cape Verde Purple Heron Ardea
( purpurea ) bournei: 10—20 pairs),
while others are now known to be
more widespread than previously
thought (e.g. Cape Verde Warbler
Acrocephalus brevirostris, recently
discovered on Fogo, with 129
territories counted there in 2006).
Submissions can be prepared in
English (with a Portuguese summary)
or Portuguese (with an English
summary). Zoologia Caboverdiana
will be published biannually, with
issues in spring and autumn. For
further information, contact the
Editor (cjhazevoet@gmail.com).
Sources: C. J. Hazevoet in litt. 2010;
Zoologia Caboverdiana 1, pp. 3—44
The origin and relatives of the
Canaries endemic pigeons
A multi-locus molecular study has
recently revealed the closest relatives
of the two endemic pigeons found
in the Canary Islands. Dark-tailed
Laurel (Bolle’s) Pigeon Columba
bollii is apparently most closely
related to the widespread Common
Wood Pigeon C. palumbus of
Eurasia, and its lineage is speculated
to be a relatively recent arrival in the
islands, 5 MYA. In contrast, Laurel
Pigeon C. junoniae was found to
occupy a position basal to the Old
World genus Columba , but of those
species sampled is perhaps most
closely related to Ashy Wood Pigeon
C. pulcbrichollis of the Oriental
region, and African Olive Pigeon
C. arquatrix. Its lineage in the
1 54 -Bull ABC Vol 17 No 2 (2010)
Africa Round-up
archipelago dates back much further,
some 20 MYA.
Source: J. Ornithol. 150, pp. 357-367
Recolonisation of Ascension
Island by seabirds after
eradication of feral cats
The introduction of cats on
Ascension Island in 1815 caused the
extinction of the once-huge seabird
colonies from the main island, with
relict populations of most species
persisting only at locations that
were inaccessible to cats. During an
eradication programme, implemented
in three phases between February
2002 and January 2006 and costing
c.UK£650,000, all feral cats — 79
in total — were killed. Five seabird
species have now recolonised the
97-km2 main island: White-tailed
Tropicbird Phaethon lepturus (25
pairs in cat-accessible sites in 2007),
Red-billed Tropicbird P. aethereus
(eight pairs), Masked Booby Sula
dactylatra (152 pairs), Brown
Booby S. leucogaster (29 pairs) and
Brown Noddy Anous stolidus (79
pairs). The numbers of each have
Masked Booby / Fou masque Sula
dactylatra (Peter Berglin)
Brown Booby / Fou brun Sula
leucogaster (Phil Palmer, www.
birdholidays.co.uk)
increased through time, although
breeding success has been relatively
low and growth of the new colonies
is likely to be slow. The roles of
food availability, inexperience of
parent birds and Black Rat Rattus
rattus predation in causing this low
reproductive output need to be
investigated.
Source: Oryx 44, pp. 20-29
Gough’s seabirds severely
threatened by mice
The devastating effect of predatory
House Mice Mus muscidus on Gough
Island has been well publicised.
Mice kill large numbers of Tristan
Albatross Diomedea ( exulans )
dabbenena and Atlantic Petrel
Pterodroma incerta chicks, causing
population declines in these near-
endemic breeders. Both species breed
in the southern winter, when the
mice have few other food sources.
Impacts on other, summer-breeding
seabirds are still poorly known.
However, anecdotal observations
by Peter Ryan, who first visited
the island in the 1980s, suggest
that the mice have caused dramatic
decreases in the populations of a
wide range of seabirds. Entries in
Peter’s notebooks mention, for a
single misty night on 24 October
1984, thousands of Kerguelen Petrels
Afrodroma brevirostris, hundreds of
Little Shearwaters Puffinus assimilis
and Grey-backed Storm Petrels
Garrodia nereis , and thousands of
individuals of five other seabirds.
Over many evenings of spotlighting
in September-October 2009, he
didn’t see a single Kerguelen Petrel,
just one Little Shearwater and two
Grey-backed Storm Petrels.
Source: Africa — Birds & Birding
15(2), p. 13
East Africa
Action needed for the Liben
(Sidamo) Lark
Urgent conservation action is now
needed to save the Liben (Sidamo)
Lark Heteromirafra sidamoensis.
This globally threatened species is
known only from the Liben Plain in
southern Ethiopia where its grassland
Liben (Sidamo) Lark / Alouette
d’Erard Heteromirafra sidamoensis
(Artur Bujanowicz)
habitat is rapidly deteriorating. The
species prefers areas with above
average grass cover and the reduction
in area of these parts in particular
has led to a 40% reduction in the
bird’s numbers in 2007-09. The
deterioration has been most severe
in areas where the species was more
widespread during the 2007 survey.
The most likely explanation is
overgrazing rather than drought. Paul
Donald and others from BirdLife
suggest that cattle should be excluded
from the main area for the bird as
soon as possible and that the area
may require ploughing to reduce soil
compaction. Longer term, removal of
encroaching scrub, reducing grazing
and developing sustainable rangeland
management are other priorities.
It should be added that all these
measures have the full and active
support of local pastoralists, so there
is some hope.
Source: Bird Conserv. Intern. 20, pp.
1-12
Karamoja Apalis on the march
Karamoja Apalis Apalis karamojae
(Vulnerable) is confined to north-
east Uganda, north-central Tanzania
and southern Kenya. In Tanzania,
it was originally known solely from
the Wembere Steppe, but since
1993 (perhaps even 1983) has
extended its range into the Serengeti,
C.140 km to the north, and it had
reached southern Kenya by 2004.
This change seems to be broadly
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Bull ABC Vol 17 No 2 (2010) -155
Karamoja Apalis / Apalis du Karamoja
Apalis karamojae (Albie Venter)
correlated to a cyclical change in the
density of its main habitat, Acacia
drepanolobium woodland, which
was low in the 1970s, high during
the 1980s and 1990s, and declined
during the early years of the new
millennium. Both the apalis and its
habitat appears to respond to changes
in grazing pressure, as increasing
Wildebeest Connochaetes taurinus
numbers have reduced the volume
of combustible material present, and
hence the frequency of damaging ‘hot
burns’. At present the bird’s range
seems to be in decline, following a
recent reduction in the density of
A. drepanolobium in the northern
Serengeti.
Source: Afr. J. Ecol. doi:
10.111 1/j. 1365-2028.2009. 01 1 74.x
Indian Ocean Islands
Amsterdam Albatross is in trouble
As if we did not know already!
Longline fishing and climate change
are affecting the viability of the
Amsterdam Albatross Diomedea
amsterdamensis. As a breeder, the
species is restricted to the upland
plateau of Amsterdam Island in
the southern Indian Ocean, and its
population was just nine pairs in
1983. Philippe Rivalan and others
have been modelling what might
happen to this Critically Endangered
population. Results indicate that
climate affects the species in both its
breeding and wintering grounds, but
that these to some degree compensate
for the impact of additive bycatch
mortality from longline fishing.
However, the models also show that
any compensation would be null
if more than six individuals were
caught on longlines each year, and
therefore if such fishing is resumed
in the areas used by the species for
feeding at any season this albatross
would be in even graver danger.
Source: Ibis 152, pp. 6-17
Southern Africa
South African vultures threatened
by World Cup
It may sound too absurd for words,
but football really can threaten the
survival of vultures. The 2010 World
Cup Football matches in South
Africa are expected to increase the
use of vulture brains in ‘muti’, i.e.
traditional medicine, by gamblers,
to help them predict match results.
Vultures’ acute vision and ability
to find prey over long distances has
led to the belief that they possess
clairvoyant powers. Gamblers
therefore smoke their dried brains in
a cigarette in the hope that this will
bring them a vision of the future — in
this case the football results.
Source: www.ewt.org.za
Langebaan Lagoon saved
Intensive lobbying by BirdLife South
Africa and its partners has saved the
internationally important wetlands of
Langebaan Lagoon and the Saldanha
Bay area, c. 100 km north of Cape
Town, from a port development.
Langebaan Lagoon is an Important
Bird Area (IBA) and Ramsar site,
and its extensive areas of mudflat,
sandflat and succulent saltmarsh
regularly support more than 34,500
waders, 93% of which are Palearctic
migrants. In the southern winter,
the lagoon supports more than
10,500 birds, among them 4,500
Greater Flamingos Phoenicopterus
{ruber) roseus and 4,000 waders.
Langebaan Lagoon is South Africa’s
most important wetland for waders,
regularly accounting for c.10% of the
country’s shorebird numbers.
Source: www.birdlife.org
African Penguins enabled to fish
closer to home
A ban on purse-seine fishing within
20 km of an African Penguin
Spheniscus demersus colony on St.
Crois Island, in Algoa Bay, South
Africa, has enabled the birds to fish
much closer to home. Penguins
were tagged and monitored before
and after the ban was enforced. It
appeared that before the ban, 75%
of the birds had to swim further
than 20 km to find food; three
months after the ban, 70% were able
to forage within the 20-km zone.
The African Penguin population
decreased by 60% between 2001
and 2009, due to a sharp decline in
anchovy and sardine stocks caused
mainly by purse-seine trawling and
climate change.
Source: Africa Geographic 1 8(3),
p. 12
Taxonomic proposals
A ‘new’ Buteo species
Richard Porter and Guy Kirwan
have described a ‘new’ buzzard
species, Buteo socotraensis (Socotra
Buzzard) from the main island of
Socotra. First collected over 1 10
years ago and initially considered of
taxonomic interest by the perceptive
Ernst Hartert almost a century ago,
the difficulties associated with Old
World Buteo systematics, coupled
with the lack of specimens (just six
are available), had prevented this
problem from being resolved until
now. Extensive field experience
proved informative in describing
the new taxon, which molecularly
is poorly differentiated from most
Socotra Buzzard / Buse de Socotra
Buteo socotraensis (R. F. Porter,
© British Ornithologists’ Club)
1 56 - Bull ABC Vol 17 No 2 (2010)
Africa Round-up
Old World buzzards, being especially
close to B. buteo bannermani
of the Cape Verdes and Long-
legged Buzzard B. rufvnus of the
southern Palearctic. In contrast, its
morphology is .similar to Mountain
Buzzard B. oreophilus , and clearly
quite different from its closest
genetic relatives. The new taxon,
which is noticeably short-winged,
has been described as a new species
to highlight its intriguing position,
both morphologically and genetically.
Socotra Buzzard’s small population
of probably <250 pairs would trigger
its immediate categorisation on the
1UCN Red Data list, should BirdLife
International decide to recognise it as
a species. Fortunately, the majority
ol birds occur within areas already
designated for protected status.
Source: Bull. Br. Ornithol. Cl. 130,
pp. 116-131
Black-collared Bulbul really is a
bulbul!
Dario Zuccon and Per Ericson,
from the Swedish Natural History
Museum, have used nuclear and
mitochondrial sequences to clarify
the phylogenetic position of the
Black-collared Bulbul Neolestes
torquatus. The data confirm that
it is indeed a member of the
Pycnonotidae (bulbuls) and that it
is actually well embedded within the
family’s Afrotropical radiation. Its
systematic position has varied over
the years, although the species has
usually been placed within or close to
the bulbuls, but doubts have persisted
largely because its striking plumage is
in complete contrast to the majority
Black-collared Bulbul / Bulbul
a collier noir Neolestes torquatus
(Jon Hornbuckle)
of African bulbul species. However,
this could be related to its habitat
preference of lightly wooded savanna,
rather than the predominantly
forest-based habitats of most other
‘greenbuls’.
Source: Ibis 1 52, pp. 386-392
Phylogeography of Green Hylia
Ben Marks, formerly of Louisiana
State University, has recently
published a phylogeographic
study of the Green Hylia Hylia
prasina , a widely distributed forest
species belonging to a monotypic
genus that occurs from Gambia to
western Kenya, including the Gulf
of Guinea island of Bioko. The
insular population {H. p. poensis) is
recognised subspecifically, principally
based on its whiter throat, which
distinguishes it from all mainland
populations. Surprisingly, Marks
uncovered previously unhinted at
genetic diversity within mainland
populations, with five highly
divergent haplotype groups that
are distributed in accordance with
broad-scale areas of endemism in
the Afrotropics. Marks suggests
that if the pattern of geographic
variation in Hylia occurs broadly in
other widespread rainforest species,
conservation policy makers might
need to rethink their priorities for
conservation in the Afrotropics.
Source: Mol. Phyl. & Evol. 55,
pp. 178-184
Genetic variation in Mascarene
White-eye
Mascarene White-eye Zosterops
borbonicus shows a striking,
geographically structured plumage
polymorphism on the topographically
and ecologically complex island of
Reunion (three subspecies, Z. b.
borbonicus, Z. b. alopekion and Z.
b. xerophilus ) yet is monotypic on
the relatively uniform neighbouring
island of Mauritius (which
population, Z. b. mauritianus , has
recently been treated specifically by
the IOC). Independent evolution
of the Reunion and Mauritius
populations is confirmed by a recent
molecular study. Furthermore,
populations on Reunion showed
significant differentiation into three
main genetic groups separating
lowland from highland areas despite
the small geographic distances
involved. Birds in the highlands
are larger but have relatively
smaller bills than in the lowlands,
suggesting the role of selection in
shaping morphology and restricting
gene flow. However, the lack of
congruence between genetic groups
and plumage morphs suggests that
the latter are of recent origin and
probably due to social or sexual
selection acting on few loci. The
presence of sharp and stable contact
zones between plumage morphs
suggests that they could be on
independent evolutionary trajectories,
yet whether or not they represent
incipient species will require further
research to directly assess the degree
of reproductive isolation.
Source: BMC Evol. Biol. 10,
doUO.l 186/1471-2148-10-158
Socotran endemics update
We recently {Bull. ABC 15: 162)
reported that a proposal to recognise
Passer insularis hemileucus, the
so-called ‘Abd Al-Kuri Sparrow, at
species level had been published.
Now genetic data, recently obtained
by Pete Ryan et al. have apparently
confirmed this distinction. BirdLife
International, in ratifying this
proposal, have recently listed this
sparrow as globally threatened
affording it the Vulnerable category,
based on its small population
(assumed to be <1,000 mature
individuals) and small range (the
island of Abd 'Al Kuri is just 133
km2). More interestingly, Ryan and
his colleagues studied the sparrows
present on the tiny islands of Darsa
and Samha, which lie closer to the
main island of Socotra, finding
some plumage and morphometric
differences that might warrant their
recognition as a subspecies of Socotra
Sparrow P. insularis.
Separately, Guy Kirwan and
Andrew Grieve studied the position
of the Socotran endemic race of
Long-billed Pipit Anthus similis
sokotrae. They found that many
previously published plumage
characters used to differentiate this
taxon are extremely marginal or
Africa Round-up
Bull ABC Vol 17 No 2 (2010) -157
incorrect, but that morphometries
can be used to delimit the subspecies.
These authors also addressed the
issue of how many subspecies
of Long-billed Pipit should be
recognised in mainland southern
Arabia, concluding that it is more
appropriate to recognise two, rather
than three, contra the suggestion of
the late Philip Clancey.
Sources: Bull. Br. Ornithol. Cl. 130,
pp. 75—82; Sandgrouse 32, pp. 43-49
Internet resources
Indigobirds website
A new website (www. indigobirds.
com) has been created to collect and
disseminate information about the
brood parasitic indigobirds ( Vidua
spp.). The multimedia website
summarises research on these birds,
along with locality records, range
maps, pictures and sound-recordings.
One of rhe primary objectives is to
increase knowledge about these birds
by collecting notes, photographs and
especially recordings of indigobird
songs from students, birders, and
both amateur and professional
ornithologists. Because indigobird
species are morphologically similar
and difficult to identify in the
field, the distributions of these
birds are poorly known. Indigobird
males, however, convey critical
information in their songs; by
mimicking their host species, males
provide an unambiguous indication
of the species that raised them.
In consequence, the website’s
creators are particularly interested
in gathering geo-referenced sound
or video recordings of indigobirds
throughout Africa. Please e-mail
them at indigos@bu.edu.
Source: Jeffrey DaCosta & Michael
Sorenson in litt. to African Birding
May 2010
Niger bird database
The new Niger bird database, in
English and French, can now be
accessed via http://www.bromus.net/
nibdab. The site promotes knowledge
and conservation of the birds of
Niger. Geo-referenced observations
can be entered, analysed and shown
on maps with a few clicks of the
mouse and minimal typing. The page
can also be used to produce site lists,
and to find out where to look for
certain species. Bird images from the
country can be uploaded, and there is
a blog facility.
Source: Joost Brouwer & UlfLieden in
litt. June 2010
New blog on birds of La Palma,
Canaries
A blog on the birds of La Palma,
Canary Islands, has been created by
Robert Burton, a keen birder and
bird photographer living on the
island. Visit http://lapalmabirds.
blogspot.com/
Source: Ruben Barone in litt.
February 2010
Request
Owls of the World— a request
for photographs
In 2012, A. & C. Black will
be publishing a definitive
photographic guide to the
world’s 250 species of owls,
and the process of sourcing and
selecting photographs is now
well underway. Owls of the World
is being written by Finnish
owl expert Heimo Mikkola,
and the publisher is inviting
photographers and birders around
the world to submit images
(preferably digital) for use in the
book, which will place particular
emphasis on plumage variation
and racial separation. Photographs
of young birds, island endemics
and adults in flight are
particularly welcome! If you can
help, please send an e-mail in the
first instance to Ellen Parnavelas
(eparnavelas@acblack.com) .
Corrigendum
The team searching for Sociable
Lapwings Vanellus gregarius in the
highlands of Eritrea in December
2009 did not find this species,
as erroneously reported in the
previous ABC Conservation Fund
news [Bull. ABC 17: 7) — they
observed only flocks of Black-
winged Lapwings V. melanopterus.
Advertise in the Bulletin of the ABC
Reach over 1,200 subscribers in more than 60 countries.
Copy deadlines
Advertisements should be submitted as high-resolution
March Bulletin 15 January
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vr
Rates and technical details
All advertisements must be prepaid: cheques made payable
are available on the ABC web site at:
to the African Bird Club or payment made via the ABC
www.afiicanbirdclub.org/club/advertise.html
website www.africanbirdclub.org.
158 -Bull ABC Vol 17 No 2 (2010)
Africa Round-up
Further ornithological exploration of Namuli and
Mabu Mountains (northern Mozambique), and the
urgent need to conserve their forests
Franco i se Dowsett-Lemaire
Nouvelles decouvertes ornithologiques dans les montagnes de Namuli et Mabu (nord du
Mozambique), et la necessite urgente de proteger leurs forets. Cet article presente les resultats de
deux expeditions recentes au Mont Namuli (novembre 2007) et au Mont Mabu (octobre 2008) au
Mozambique, au cours desquelles plusieurs especes menacees et d’interet biogeographique ont ete
decouvertes. Des corrections sont apportees a la liste des oiseaux presentee pour Namuli par Ryan et al.
(1999a), et les densites d’especes proposees par ces auteurs sont revues nettement a la baisse. Le massif de
Mabu est recouvert de la plus grande foret d’altitude moyenne de la region, c.60-70 km2 entre 1.000 et
1.650 m. Cette foret est assez peu menacee contrairement aux fragments qui subsistent a Namuli, a plus
haute altitude (principalement 1.600-1.900 m) et totalisant environ 13 km2. Bien que P Apalis de Namuli
Apalis ( thoracica ) lynesi et la Grive-akalat tachetee Modulatrix orostruthus viennent d’etre decouvertes a
Mabu, elles y sont tres rares, done il est urgent de sauver ce qui reste de la foret de Namuli ou ces especes
sont nettement plus communes. La foret de Mabu, par contre, est tres importante pour la sauvegarde de
1 Alethe de Cholo Alethe choloensis et la race belcheri du Barbican olivatre Stactolaema olivacea (deux especes
beaucoup plus nombreuses qu’a Namuli), ainsi que de l’Akalat de Swynnerton Swynnertonia swynnertoni
(nouveau pour le nord du Mozambique) et l’Akalat de Gunning Sheppardia gunningi. La Grive terrestre
tachetee Zoothera guttata niche probablement dans les deux massifs. La foret de Mabu abrite aussi les plus
importantes populations au niveau regional du Pigeon de Delegorgue Columba delegorguei , Calao a joue
argent Bycanistes brevis , Barbican olivatre, Echenilleur gris Coracina caesia et Loriot a tete verte Oriolus
chlorocephalus. Quelque 127 especes sont connues de Mabu.
Summary. Several species of conservation concern or biogeographical interest were discovered during two
recent expeditions to Mount Namuli (November 2007) and Mount Mabu (October 2008) in Mozambique.
Corrections are made to the list of species presented for Namuli by Ryan et al. (1999a), and densities of
species proposed by the same authors must be revised downward by a factor of 5-30. The Mabu massif is
covered with the most extensive mid-altitude rain forest in the region, of c.60-70 km2 between 1,000 and
1.650 m. This forest is not seriously threatened at present, unlike those higher altitude remnant fragments
on Namuli (mainly at 1,600-1,900 m), totalling some 13 km2. Although Namuli Apalis Apalis ( thoracica )
lynesi and Dapple-throat Modulatrix orostruthus have recently been discovered on Mabu, they are very rare
there and it is therefore urgent to save the forest remnants on Namuli where these two species occur at
much higher densities. The forest on Mabu is, on the other hand, of the utmost importance for preserving
the endangered Cholo Alethe Alethe choloensis and the race belcheri of Green Barber Stactolaema olivacea, as
these two species are much more numerous than at Namuli, as well as Swynnerton's Robin Swynnertonia
swynnertoni (new for Mozambique) and East Coast Akalat Sheppardia gunningi. Spotted Ground Thrush
Zoothera guttata probably breeds on both massifs. Mabu Forest holds the most important regional popula-
tions of Eastern Bronze-naped Pigeon Columba delegorguei. Green Barber, Grey Cuckooshrike Coracina
caesia and Green-headed Oriole Oriolus chlorocephalus. Some 127 species are known to occur at Mabu.
Mount Namuli is the largest massif in
Mozambique north of the Zambezi, with
a granitic dome rising to 2,419 m. It lies 160 km
north-east of Mount Mulanje in Malawi (3,002
m), the tallest mountain in south-central Africa.
Mount Mabu, situated 160 km south-west of
Namuli and 90 km south-east of Mulanje, is lower
(peak 1,710 m) but more extensively forested;
it is 70 km east-north-east of Mount Chiperone
(2,054 m), the second-tallest massif in northern
Mozambique (Fig. 1). Mulanje has the widest
altitudinal range of forest, from 700 to 2,300
m, but the largest block of forest on the wetter,
south-eastern slopes was illegally destroyed lor
farms, up to the level of 1,600 m; total forest
cover was recently estimated at just less than 70
Ornithological exploration of Namuli and Mabu Mountains: Dowsett-Lemaire
Bull ABC Vol 17 No 2 (2010) -159
Figure 1. Map showing main massifs in southern Malawi
and adjacent Mozambique.
Carte montrant les principaux massifs montagneux du sud
du Malawi et Mozambique voisin.
Figure 3. Summit of Mount Namuli, with Ukalini Forest
in the saddle below (Jonathan Timberlake)
Sommet du Mont Namuli, avec la foret d’Ukalini sur le
replat en dessous (Jonathan Timberlake)
Figure 5. Extensive undulating forest on Mount Mabu,
asseen from near the peak (Julian Bayliss)
La foret du Mont Mabu s’etend a perte de vue, comme
ici pres du sommet (Julian Bayliss)
Figure 2. Part of Manho Forest, the largest patch on
Namuli (Jonathan Timberlake)
Une partie de la foret de Manho, le bloc le plus etendu a
Namuli (Jonathan Timberlake)
Figure 4. Muretha Plateau, with mosaic of forest patches
and grassland, and Namuli peak in the background
(Frangoise Dowsett-Lemaire)
Plateau de Muretha, avec mosai'que de petites forets et
prairies, et le sommet de Namuli au fond (Franchise
Dowsett-Lemai re)
Figure 6. Specimens of Bar-throated Apalis Apalis
thoracica of the subspecies flavigularis (above) and of
Namuli Apalis Apalis ( thoracica ) lynesi (Lincoln Fishpool ©
Natural History Museum, Tring)
Specimens de T Apalis a gorge barree Apalis thoracica de la
race flavigularis (en haut) et de I’Apalis de Namuli Apalis
(. thoracica ) lynesi (Lincoln Fishpool © Natural History
Museum, Tring)
160 - Bull ABC Vol 17 No 2 (2010)
Ornithological exploration of Namuli and Mabu Mountains: Dowsett-Lemaire
krrr (Dowsett-Lemaire & Dowsett 2006: 81).
The forest remaining around Namuli peak covers
c. 13 km2, most of it above 1,600 m. The forest
on Mabu, covering 60-70 km2 at elevations of
c. 1,000 to 1,650 m, represents the largest single
block of mid-altitude forest in Mozambique and
in the wider region.
While Mount Namuli has been visited by
several ornithologists, commencing with Vincent
in 1932 (Vincent 1933, 1933-36), and followed
by Ryan et al. (1999a, 1999b), the avifauna of
Mabu was entirely unknown until December
2005, when C. Spottiswoode and colleagues spent
four days in the foothills and lower slopes, up to
1,220 m (Spottiswoode et al. 2008). In 2007-08
a multidisciplinary team of scientists supported
by the Darwin Initiative (UK) visited Namuli
and Mabu. Demey (2007) took part in the first
expedition to Namuli, on 22 May-5 June, while I
was part of the second, on 14-27 November 2007,
and participated in the survey of Mabu on 1 0-30
October 2008, with R. J. Dowsett and L. D. C.
Fishpool (the latter on 17-29 October only).
In November 2007, K. Cook from the Natural
History Museum, Tring, collected 49 birds of 20
species on Namuli. It should also be mentioned
that staff from Chicago’s Field Museum collected
birds at Namuli in July-August 2003, and for
three months in 2004, based on Muretha Plateau
(J. Bayliss in lift. 2009). The results of these
collections have never been published, but a list of
specimens for 2003 was placed on the museum's
website (http://fml.fieldmuseum.org/birds/brd_
index. php, accessed 30 January 2008); details of
the 2004 collections remain unavailable.
Vincent collected two bird species new to
science on Namuli: the enigmatic Dapple-throat
Modulatrix orostrutbus and Namuli Apalis Apalis
(tboracica) lynesi. The latter is a close relative of
Bar-throated Apalis A. thoracica and until recently
was considered endemic to Namuli; the former is
represented by the nominate form, another two
races having been discovered subsequently on
mountains in central and northern Tanzania (Keith
et al. 1992). Vincent also discovered populations
of the (now) Endangered Cholo Alethe Aletbe
cboloensis (a species endemic to south-eastern
Malawi and adjacent Mozambique) and of the
race belcheri of Green Barbet Stactolaema olivacea,
shared with I hyolo Mountain in southern Malawi,
which is now almost wholly deforested (Dowsett-
Lemaire & Dowsett 2006). From a week’s survey
in late 1998, Ryan et al. (1999a, 1999b) proposed
exceptionally high density estimates of the more
frequent bird species. Two other visits (by M.
Melo et al., in December 2001, and R. Demey)
were respectively too short or at the wrong season
to study bird densities. Thus, one of the main
purposes of the present survey was to re-evaluate
the densities of those key species for which the
conservation of Namuli is especially important.
The preliminary survey of Mabu by
Spottiswoode et al. (2008) located two threatened
bird species, Cholo Alethe and East Coast Akalat
Sheppardia gunningi, but much remained to be
explored, especially at higher altitudes. October,
at the end of the dry season, was chosen for
this survey for at least two reasons: it normally
coincides with the start of the breeding season
in this part of Africa ( cf. Dowsett-Lemaire &
Dowsett 2006) and it was hoped that access and
exploration would not be impaired by heavy rain.
Notes on selected species are followed by a full
list of bird species recorded at Mabu (Appendix
2), preceded by a Gazetteer (Appendix 1). Ryan et
al. (1999a) presented a consolidated species list for
Namuli; some important additions or corrections
are mentioned here; others are given in Dowsett-
Lemaire (2008b).
Site description and location of surveys
Namuli
The massif is part of a fairly extensive plateau 40
x 50 km wide, at 1,100-1,200 m, rising above
the peneplain at 600-700 m. Access is via the
small town of Gurue, on the southern side. From
the tea estates above Gurue a rough road leads to
the Malema River, met at an altitude of 1,250 m.
The vegetation is a mosaic of forest, grassland and
large granitic domes. The semi-forested plateau
south of the Malema Valley has yet to be explored
by any naturalist and the remnant forest patches
there are in the process of being destroyed by
shifting cultivation and fires. The forest nearer the
peak, visited by Vincent and others, is of the order
of 1,300 ha, most of it comprising a large dissected
block on the south-western slopes of Muretha
Plateau called Manho Forest, c. 1,000-1,100 ha
in extent (Fig. 2). Manho Forest is typically
Afromontane, dominant emergent trees at 1,600-
1,850 m being Cryptocarya liebertiana , Faurea
Ornithological exploration of Namuli and Mabu Mountains: Dowsett-Lemaire
Bull ABC Vol 17 No 2 (2010) -161
wentzeliana and Olea capensis (25-30 m tall). The
second-largest block of forest lies in the Ukalini
saddle, lodged against the base of the Namuli
dome itself, at 1,580-1,750 m, with galleries
ascending to c. 1,900 m: the whole covers r.100 ha
(Fig. 3). The most extensive grassland (c.170 ha)
is on Muretha Plateau at 1 ,800—1 ,900 m. Much
of this is seasonally water-logged, on black peaty
soil, and the tussocky nature of this grass makes
walking very difficult, except on old game tracks
now used by domestic goats. Muretha Plateau is
dotted with small forest patches (in which Myrica
humilis, Prunus africana and Syzygium cordatum
are common), often of 1-2 ha (Fig. 4). Montane
shrubland is of limited extent and floristically
poor, patches of bracken Pteridium aqudinum also
occur in the vicinity of forest or on slopes above
the wet grassland.
Strips of riparian forest (with Albizia
adianthifolia, Newtonia buchananii and Parinari
excelsa the dominant large trees) occur on the
lower slopes, mainly at 1,150-1,450 m, e.g. along
the Malema River, and the Nanchili stream that
descends from Ukalini. These mid-altitude forests
were formerly more extensive, but had already
been greatly reduced by the late 1960s, when
aerial photos were taken. They continue to regress
as a result of fires and direct logging; in November
2007 some new maize fields had been planted
in place of forest right beside the Malema and
Nanchili streams. Away from the forested gullies
some trees have survived the fires and locally
form a type of evergreen woodland dominated
by Syzygium cordatum-, this Syzygium may form a
closed canopy adjacent to riparian forest. Syzygium
woodland is what was called ‘miombo’ by Ryan et
al. (1999a, 1999b, cf their photo 2), but there is
no miombo ( Brachystegia ) woodland on Namuli.
Vincent (1933) camped from 21 July to 10
August 1932 at 1,400 m on the Nanchili stream,
just below the Ukalini shelf. He collected c.250
specimens of 53 species from 1,370 m to nearly
2,000 m, and made observations on an additional
dozen species. Ryan et al. (1999a, 1999b) visited
on 27 November-4 December 1998, using two
different camp sites on the Nanchili stream (at
1,170 and 1,250 m), and one at the lower edge of
Ukalini Forest. From Ukalini, they spent one day
visiting Muretha Plateau.
In 2007 our base camp was located on
Muretha Plateau, at 1,860 m, for nine days
(15-23 November), from where Manho Forest
and several small patches on the plateau were
investigated. In addition two nights were spent
in Ukalini Forest, and two on the Malema River
at 1,250 m, during which time I also explored
riparian forest on the Nanchili stream. There were
four big storms during our stay.
Mabu
The peak comprises a granite dome which, together
with a few other granitic formations, rises above a
sea of undulating forest (Fig. 5). The lower slopes
are covered in transition woodland, riparian forest
(down to at least 300 m), cultivation and a large
expanse of neglected tea plantations (deserted in
the early 1980s). The latter have developed into
dense tea forest ( Camellia sinensis ) 10-12 m tall,
overtopped by indigenous forest trees (mostly
Albizia adianthifolia). Transition woodland is
dominated by Pterocarpus angolensis at low levels,
gradually replaced with increasing altitude by the
evergreen Syzygium cordatum, up to the lower
edges of the forest block around 950 m. The
limit between mid-altitude and Afromontane
rain forest is clearly around 1,350-1,400 m,
as shown by a sudden change in tree and bird
species composition. Some large trees occur
throughout (e.g. Chrysophyllum gorungosanum,
Cryptocarya liebertiana , Drypetes gerrardii, Parinari
excelsa, Polyscias fulva and especially Strombosia
scheffleri, the commonest species), while Newtonia
buchananii and Maranthes goetzeniana drop out
just above 1,400 m, Albizia adianthifolia drops
out just above 1,350 m (to be replaced higher
by A. gummifera) and Olea capensis appears at
1,350-1,400 m. Typical montane trees near the
upper edges (1,600-1,650 m) include Pittosporum
viridiflorum, Prunus africana and Rapanea
melanophloeos. Canopy height gradually decreases
from 40-45 m around 980-1,000 m to 25-30
m around 1 ,400 m. There are several permanent
rocky streams in the forest, lined with Cyathea
tree ferns and huge Oreobambos bamboos. Most
of the large block of forest lies between 1 ,000 and
1,400 m; overall forest cover above 1,400 m is of
the order ol 800 ha (J. Bayliss in lift. 2009). Small
patches of montane shrubland grow around the
base of the peak; large boulders and rocky slopes
are covered by scattered tufts of grass.
Spottiswoode et al. (2008) spent 10-14
December 2005 at Mabu, shared between the tea
1 62 - Bull ABC Vol 17 No 2 (2010)
Ornithological exploration of Namuli and Mabu Mountains: Dowsett-Lemaire
and other lowland forest and the lower slopes of
the main forest. In October 2008, 1 spent four
nights at an altitude of 540 m by the old tea estate
manager’s house (10-12 and 29 October) when
riparian forest, mixed tea forest and transition
woodland were explored, and 16 nights in the
rain forest, mainly around 1,000 m (‘main forest
camp’), with four nights also at higher levels
(satellite camps near the summit at 1,400 m, and
at 1,300 m north-west of the main camp). The
weather was hot and dry, with the first rains falling
on 21 and 26/27 October.
Notes on selected bird species
The category of threat for Red List species is based
on BirdLife International (2008).
Southern Banded Snake Eagle Circaetus
fasciolatus
Near Threatened. Mabu: this Eastern endemic
was heard and seen on most days between 400
and 1,500 m (at forest edges below the peak), but
mostly below 1,000 m. In forest and transition
woodland. Often sings perched early morning
(calling from 04.30 hrs until daybreak), and in
display- flight in the warm hours of the day. Tape-
recorded. Unrecorded from adjacent Malawi,
its discovery at Mabu represents a small range
extension: the nearest record is from Mopeia in
the Lower Zambezi Valley (Hanmer 1976).
Crowned Eagle Stephanoaetus coronatus
No record on Namuli since Vincent (1933-36) in
1932, but, despite Ryan etal.'s (1999a) misgivings,
one pair was still holding a territory over Manho
Forest in November 2007. Given the size of the
forest and the enormous territories of Crowned
Eagles, it is unlikely there is more than one pair
in the area. Common over Mabu Forest, which is
likely to hold several pairs.
Falcons Falco spp.
There is a neat separation of home ranges between
the three breeding Falco species at Namuli. A
pair of Common Kestrels F. tinnunculus was
feeding two full-grown juveniles on a small
rocky outcrop above Manho Forest at 1,820 m
(17-20 November); another was seen between
Muretha and Ukalini. A pair of Lanner Falcons F.
biarmicus was occupying a territory over another
part of Manho Forest and adjacent grassland,
around a rocky pinnacle where they were probably
breeding; very aggressive towards other Lanners
and larger raptors (e.g. a Booted Eagle Hieraaetus
pennatus was attacked on 16 November). A pair
of Peregrine Falcons F. peregrinus was breeding on
the cliff of Namuli peak directly above Ukalini,
with prey brought to a partner or noisy young
several times daily. Ryan et al. (1999b) had
noted Peregrine in the same area. At Mabu, only
Peregrine was seen around the peak.
Guineafowls
Crested Guineafowl Guttera pucherani is well
known to local hunters at Mabu from forest
patches at low altitude, up to c. 1,000 m. We
did not encounter this species, which is much
hunted and decreasing, and in danger of being
exterminated. At Namuli, Helmeted Guineafowl
Numida meleagris was encountered regularly in
mid-altitude and montane forest, throughout, at
1,270-1,900 m. This is very unusual habitat for
the species: is it possible that guineafowls have
been pushed into marginal montane habitat by
hunting pressure?
Flufftails Sarotbrura spp.
Striped Flufftail S. affinis was reported from
Namuli by Ryan et al. (1999a, 1999b), based
on a bird seen in flight on Muretha Plateau.
The observer (P. Ryan in litt. 2008) agrees that
this record (repeated in Parker 2001) requires
confirmation. Although Melo et al. (n.d.) cite
the same species, their record is based on a
female flushed and unidentified as to species
(M. Melo pers. comm.). The only flufftail I
found on Muretha Plateau is Red-chested S. rufa,
which was heard on several occasions in the wet
meadows with tall grass near the stream at base
camp, and further up the valley where it appeared
common. Other species characteristic of this wet
type of grassland on Muretha include Broad-tailed
Warbler Schoenicola brevirostris and Red-collared
Whydah Euplectes ardens. Playback experiments
with the songs and calls of both Sarotbrura elicited
responses from Red-chested only (tape-recorded);
the characteristic territorial calls ( kuwa-kuwa -
kuwa . . . ) were even imitated by an Olive Thrush
Furdus olivaceus in its song. Thus it is probably the
only flufftail on Muretha; the dry or well-drained
montane grassland favoured by Striped Flufftail in
the tropics is hardly available at Namuli. Striped
Ornithological exploration of Namuli and Mabu Mountains: Dowsett-Lemaire
Bull ABC Vol 17 No 2 (2010) -163
Flufftail is known from montane grassland in the
Chimanimani Mountains (Masterson & Child
1959), but it is not clear whether it has been
recorded irom the Mozambique side, and there
is more grassland on the Zimbabwe side. In other
words, rhe occurrence of Striped Flufftail in
Mozambique remains unproven.
Pigeons Columba spp.
Eastern Bronze-naped Pigeon Columba delegorguei.
Discovered by Spottiswoode et al. (2008) in
the foothills of Mount Chiperone, this species
also occurs on Mabu, in small numbers. It was
widespread in the forest canopy at 980-1,420
m. Vocal activity apparently decreased from mid
October. Following deforestation at Thyolo, it
is now extinct in Malawi, where it was probably
no more than a scarce seasonal visitor (Dowsett-
Lemaire & Dowsett 2006). The origin of the
Thyolo birds was probably from this Mozambique
population, still a long way from the nearest
previously known populations in eastern Zimbabwe
and on Mount Gorongosa (Irwin 1981, Oatley
& Tinley 1989) and in central Tanzania on the
Udzungwas (Stuart & Jensen 1987).
At Mabu there is very little altitudinal overlap
with Rameron Pigeon C. arquatrix , a specialised
montane frugivore which was found feeding at
1,350-1 ,400 m and above on the fruits of Polyscias
and Olea. As the great majority of Olea capensis
were flowering, this pigeon's population would
be expected to increase the following year (as Olea
fruit bi-annually, see also Dowsett-Lemaire 1988).
It is curious that in 2007 Olea were also at the
flowering stage at Namuli, thus ‘olive years’ seem
to occur in alternate years on Namuli and Mabu.
Selected swift species
The most numerous swift over Namuli was African
Black Swift Apus barbatus, which was seen daily
sometimes in hundreds. Often feeding low down
over rhe lip of Muretha Plateau, and over rock
faces. In November breeding was well advanced:
four pairs were feeding noisy fledglings in a cleft
on a small vertical cliff above Manho (1,840 m, 20
November). In addition to the characteristic rasping
screams of adults, the calls of recently fledged birds
tititititi were heard in many flocks. By contrast,
Scarce Swift Schoutedenapus myoptilus , an intra-
African migrant, breeds later: aerial mating was
observed on 20 November over Manho Forest.
Although Ryan et al. (1999a) did not report
African Black Swifr, nor did they include it in
the table summarising previous records, Vincent
(1933-36) had noted the species as common
at 1,500-2,100 m. Neither of these two swifts
was found at Mabu. Scarce Swift, in particular,
could be expected to occur but the arrival of this
noisy bird was perhaps delayed by the prolonged
drought in the area. In adjacent Malawi most
birds seen in September-October are on passage,
and they do not settle in a forested area until
the rains set in; aerial copulation was observed
there from late October to December (Dowsett-
Lemaire & Dowsett 2006).
Silvery-cheeked Hornbill Bycanistes brevis
No records at Namuli before November 2007,
when singles or pairs were located at mid and
high altitudes on three dates, possibly just passing
through. Ryan et al. (1999a) recorded the species
in a patch of forest near Gurue (1,400 m). A much
larger population exists at Mabu, at 500-1,600
m. Much movement of pairs or family groups was
noted across the forest, as, for example, near the
main camp where they fed in a fruiting Sapium
ellipticum , and some ate figs of Ficus scassellatii at
1 ,400 m. Appeared not to be breeding in October,
when the quantity of fruit in the forest was low
since, in particular, most strangler figs were not
in fruit (whereas they are in Malawi at this time).
The population of this hornbill has dwindled
considerably in the region due to much recent
deforestation in southern Malawi, so Mabu has
acquired a special importance for the species.
Green Barbet Stactolaema olivacea
Heard by Spottiswoode et al. (2008) at Mabu,
the species was common in the main forest at all
elevations, with a few pairs also in riparian patches
lower down (to 750 m). A pair observed at close
range around a nesr appeared to be of the race
belcheri of Thyolo and Namuli (dark blackish
head, dark olive breast contrasting with olive belly,
pale brown patch behind eye inconspicuous).
Mabu thus harbours the most important
population of this distinctive race, in the order of
several hundred pairs (probably >500). Details of
brooding and feeding behaviour can be found in
Dowsett-Lemaire & Dowsetr (2009).
The population at Namuli is much smaller,
probably just 30-40 pairs. The species is common
1 64 - Bull ABC Vol 17 No 2 (2010)
Ornithological exploration of Namidi and Mabu Mountains: Dowsett-Lemaire
in the small Ukalini Forest, but scarce at Manho:
only four occupied territories were located there,
along the ‘circuit route’ crossing the whole forest.
The distance between the first two territories
was 700 m. There is little doubt that Green
Barbets must have been formerly more numerous
at Namuli, when mid-altitude forest was more
extensive. Four ol Vincent s eight specimens were
collected at 1,400-1,500 m (K. Cook in litt.
2008), in what Vincent (1933-36) described as
thick jungle or high forest, an area where today
there is only narrow riparian forest.
Eastern Green Tinkerbird Pogoniulus simplex
Discovered on Namuli in November 2007, but
scarce. One bird (tape-recorded) held a territory
in Manho Forest at 1,720 m, covering a large
area (at least 10 ha), and another was heard in
Parinari-Syzygium cordatum forest above Nanchili
stream at c. 1,300 m. The species was not found
on Mabu where, curiously, playback at 900 m
provoked a strong vocal reaction from a Yellow-
rumped Tinkerbird P. bilineatus. This may be the
result of the superficial resemblance between the
staccato song of Eastern Green and the rolled call
of Yellow-rumped, or it might mean that Eastern
Green exists somewhere in the area (but, if so, it
must be rare).
There is only one previous record from
Mozambique, in coastal forest in the south (a
specimen from Inhambane District, 2434C1:
Clancey 1971, 1996, repeated in Parker 1999).
The nearest population known at present is in
the highlands of Mangochi and Namizimu in
south-east Malawi, which form the western limit
of the species’ range (Dowsett-Lemaire & Dowsett
2006). This area is very rich in mistletoes and
the bird is very common there; it may be that its
scarcity on Namuli is due to the lower diversity and
abundance of mistletoe species. Its close relative,
Moustached Green Tinkerbird P. leucomystax ,
a proven mistletoe specialist (Dowsett-Lemaire
1988), reaches the southern limit of its range on
Mount Mulanje, where it is also scarce, being
confined to mid altitudes where several mistletoe
species occur.
Pallid Honeyguide Indicator meliphilus
At Mabu two were found singing in forest patches
below the tea house (450 m), one in an emergent
Newtonia and the other in Albizia adianthifolia
and Newtonia , only c.500 m apart. Also, one heard
singing in the main forest, at c. 1 ,000 m. Its closest
relative, Willcocks’s Honeyguide I. willcocksi of
West-Central Africa, also favours the canopy of
large Mimosaceae for its song posts (Dowsett-
Lemaire 2008a).
Grey Cuckooshrike Coracina caesia
This Afromontane near-endemic was discovered
at Mabu in 2008, a few pairs being located in
forest canopy at 1,000-1,400 m. In southern
Malawi, the species is almost confined to Thyolo
Mountain, where it is now virtually extinct.
Otherwise C. caesia is known in the region only
from Mount Chiperone (Benson 1950), 70 km
distant.
Eastern Mountain Greenbul Andropadus
nigriceps
This high-montane species reaches the southern
limit of its range on the tallest massifs of south-
east Malawi (Zomba / Malosa and Mulanje), and
is very locally common on Namuli, but absent
from Mabu. The main population on Namuli is
to be found in a dozen small patches on Muretha
Plateau, and at the edges of Manho Forest at
1,800-1,900 m (it is absent from the interior of
Manho); it was not found at Ukalini or lower
down. On Muretha single pairs occupied patches
of 1.0-1. 5 ha. These patches also contained single
pairs of Stripe-cheeked Greenbul A. milanjensis,
and the two species appear to be in competition.
Males of both Andropadus occupied different song
posts, and seemed to engage in counter-singing
and to ‘control’ different sections of the forest
fragments {n= 4 patches, studied over a period
ol 14 hours). On the south-west Nyika Plateau
and elsewhere in Malawi where Stripe-cheeked
Greenbul is absent, the numbers of Mountain
Greenbul are twice as high as where its congener
also occurs (Dowsett-Lemaire 1989).
Overall, the population of this species must
be quite low. Proof of this comes from the fact
that K. Cook's mist-nets on Muretha caught just
one Mountain Greenbul but at least nine Stripe-
cheeked. Vincent (1933-36) had collected only
five Mountain Greenbuls compared with 2 1 Stripe-
cheeked, down to 1,400 m: this lower altitude
suggests that some had undertaken altitudinal
movements in the cold months, as also observed
with a few birds in Malawi (Dowsett-Lemaire &
Ornithological exploration of Namuli and Mabu Mountains: Dowsett-Lemaire
Bull ABC Vol 17 No 2 (2010) -165
Dowsett 2006). Stripe-cheeked Greenbul, on the
other hand, is numerous on Namuli, from 1,250
m to 1 ,900 m; it is also common overall on Mabu,
with few at 1,030-1,100 m, but becoming very
common higher, especially at 1,400-1,650 m.
Swynnerton’s Robin Swynnertonia swynnertoni
Vulnerable. Discovered at Mabu where this
montane robin occupies the higher levels of the
main forest from 1,340-1,400 m to the upper
limits. Unlike White-starred Robin Pogonocichla
stellata , the species is not uniformly distributed,
as it favours dense undergrowth with a high
density of saplings or rank growth near streams.
Some pairs were alarm-calling persistently (23-
26 October), suggesting breeding had started.
Reacted well to playback of its own song, but
not to that from eastern Zimbabwe (on Gibbon
1991), which is similar in pattern but different in
motif. The total population on Mabu, in r.800 ha
of forest, may be 100-200 pairs.
The nearest known populations are in
eastern Zimbabwe (Irwin 1981) and adjacent
Mozambique (including Gorongosa: Oatley &
Tinley 1989) and the Udzungwa highlands of
central Tanzania (Anderson et al. 1997), thus its
discovery on Mabu partly fills the gap between
the two extremes. Mabu is c.350 km north-east
of Gorongosa.
East Coast Akalat Sheppardia gunningi
Near Threatened. An Eastern endemic with a
patchy distribution horn coastal Kenya to coastal
Mozambique, and an inland population on the
northern shore of Lake Malawi and the eastern
scarp of the Viphya Plateau. First discovered on
Mabu by Spottiswoode et al. (2008) in 2005, it
was locally common in pure or mixed tea forest
(under indigenous canopy), dense understorey
and thickets in secondary forest (400-900 m) and
in the main forest block up to 1,350 m, where
it favours gullies and slopes just above streams.
In Malawi, East Coast Akalat and White-starred
Robin are locally allopatric when breeding, the
latter replacing the former at higher altitudes
(Dowsett-Lemaire 1989). This also seems to be
the case on Mabu where White-starred Robins
occur from and above 1,350 m. Territories can
be quite small (0. 5-1.0 ha) but suitable habitat is
patchy; hence it is difficult to estimate population
size, but there may be >500 pairs. The fairly
richly coloured underparts and measurements
of the Mabu birds (wing-lengths of two females
68 and 69 mm, two males 74 and 76 mm, mean
71.7 mm compared to a mean of 71.3 mm from
nine birds in Malawi: R. J. Dowsett) suggest that
they are more closely related to the race bensoni
of northern Lake Malawi than to coastal races,
despite that the nearest population to Mabu,
belonging to the nominate race, is south of the
Zambezi near the Mozambique coast at c. 18°S
(Collar & Stuart 1985, Parker 2005). Birds at
Mabu reacted well to playback of their own song,
and also to the slightly different dialect from
Malawi, but not to the dialect from coastal Kenya
(tested twice with one bird).
Fishpool (2010) has since found East Coast
Akalat on Mount Inago, 45 km north-east of
Namuli (where it is unknown), in forest patches at
1,050-1,450 m, but the area has already suffered
much deforestation as it is widely cultivated.
The akalat population of northern Malawi is
also locally threatened by deforestation, as the
integrity of official forest reserves may not be
respected: Kalwe Forest Reserve on the lakeshore
has just been cleared to build a hospital (S.
Bearder in lift. 2009). The coastal forests of
southern Mozambique, including around Dondo,
are disappearing fast (El. Chittenden in litt. 2005).
Thus, the forest at Mabu is an important refuge
for this species.
Cholo Alethe Alethe choloensis
Endangered. This ant-following specialist is very
unevenly distributed on Namuli: it is common
in Ukalini (at 1,600-1,750 m), where it reaches
densities close to the optimum of perhaps two
pairs / 10 ha. The foraging activity of army ants
was indeed high in Ukalini. The situation is very
different in the cooler forest of Manho, where
only three pairs were located along 1.5 km of trail
on the ‘circuit route’, on each of three different
days. I did not come across any ant swarms in
Manho. On Muretha, two patches (one of 1.5
ha) were each occupied by a territorial bird. At
lower altitudes, at 1,200-1,400 m, it must have
been common in the past, where the species is
still found today, but the habitat is almost gone.
Ryan et al. (1999a) proposed an astonishing figure
of over 1,000 pairs for Namuli, based on counts
along the Nanchili stream and in Ukalini. This
figure appears seriously inflated, and there may be
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Ornithological exploration of Namuli and Mabu Mountains: Dowsett-Lemaire
several reasons for this: inherent methodological
problems (see below), the fact that Ryan et al.
made their counts at low altitude (where there is
a problem of deforestation, hence over-crowding)
and in Ukalini, while not taking into account that
the situation in the much larger Manho Forest
is very different. The population on Namuli
(excluding the plateau south of the Malema River,
which is unexplored) is probably <50 pairs.
Although Ryan et al. (1999a) wrote that Cholo
Alethes near the Nanchili occasionally fed in ‘dense
Brachystegia woodland outside of forest’, as there
is no such woodland it is assumed they meant
the evergreen Syzygium cordatum formations,
which have a closed canopy immediately next to
Newtonia / Parinari forest on the Nanchili {cf site
description above). This inaccurate statement was
repeated by Collar (2005). Cholo Alethes are not
known to enter woodland of any kind.
On Mabu, fortunately, Cholo Alethes are
much more numerous, and the species covers
a wide altitudinal range of 950-1,650 m. It is
common above 1,200 m, although not evenly
distributed below this elevation. The population
is probably at least 1 ,000 pairs. On Mabu, alethes
have a most distinctive contact call, a whistle
rising in pitch, whereas elsewhere (Malawi and
Namuli) the main contact call is a downward-
inflected whistle. It was frequently heard at dawn
near the main forest camp.
Orange Ground Thrush Zoothera gurneyi
Very common on Namuli, at 1,580-1,900 m,
including Ukalini, the whole of Manho, and even
in some small patches on Muretha. This thrush
readily reacted to playback of its own song, but
also to the ‘long song’ of Spotted Ground Thrush
from Thyolo (obtained by E. Herrmann), which
is indeed inseparable from that of its own species.
Apparently absent from Mabu: repeated playback
of Orange Ground Thrush elicited no reaction, at
a time when the species (if present) would have
been very vocal.
Spotted Ground Thrush Zoothera guttata
Endangered. Previously known from Mozambique
from only two recent records on the coast near
Maputo (Parker 2005: 310), where the species
is presumably a non-breeding visitor. The few
breeding localities known are in mid-altitude
forest (e.g. in southern Malawi, and at Ngoye
in Natal) and in the temperate forests of the
Eastern Cape (H. Chittenden in Hockey et al.
2005). Rare in its tropical range (the breeding
locations of birds spending the non-breeding
season on the Kenyan coast are still unknown!)
but common locally in eastern South Africa.
Discovered on Namuli in November 2007, based
on one seen in Ukalini Forest, and a three-note
song tape-recorded in Manho on 18 November,
at 1,720 m. This song is well known to local
hunters as belonging to the ‘bird with spots’, and
is indeed similar to the ‘short song’ produced by
this species in Natal, or in Malawi (Lisau: pers.
obs.). The scarcity ol this thrush on Namuli
could be explained by competition with Orange
Ground Thrush, as is also possibly the case in
southern Malawi. However, no such explanation
can be given to explain a similar sratus on Mabu:
a Zoothera ‘long song’ was heard just after the
first rains, at two locations, at 1,000 m (28
October) and at 1,300 m (27 October). A local
hunter familiar with several bird species identified
Spotted Ground Thrush using Chittenden (2007)
without hesitation, and also indicated that Orange
Ground Thrush was unknown to him; he readily
identified Cholo Alethe on the same plate as
being common. Some ol the local people appear
to possess an outstanding knowledge of birds: all
four hunters interviewed at Namuli knew both
Orange and Spotted Ground Thrush; one hunter
at Namuli identified without prompting all four
species of apalis present on the plates of the field
guide. Jali Makawa, Benson’s gifted collector,
came from this part of Mozambique.
The discovery of this species on Namuli and
Mabu in the breeding season is the first indication
that the species breeds in the mountains of
Mozambique.
Olive Thrush Turdus olivaceus
Like Eastern Mountain Greenbul, this is another
high-montane species in this part of Africa
(Dowsett-Lemaire & Dowsett 2006), and is
apparently absent from Mabu, and very local on
Namuli. It seems to be confined to some of the
small patches on Muretha: in addition to a pair
collected by K. Cook, I located just one other pair,
and one unmated male which sang at all hours
of the day. However, a few more distant patches
on Muretha and above Ukalini were not visited.
The unmated bird occupied two adjacent patches
Ornithological exploration of Namuli and Mabu Mountains: Dowsett-Lemaire
Bull ABC Vol 17 No 2 (2010) -167
totalling just under 3 Ha; it frequently imitated the
song of Namuli Apalis and the territorial calls of
Red-chested Flufftail in its song (tape-recorded).
The second male also imitated the apalis. The
fact that the unmated male failed to attract a
female for the duration of our stay, at the height
of the breeding season, suggests a lack of surplus
individuals. Vincent (1933-36) took only one
specimen, so the species was probably always
rather scarce.
Namuli Apalis Apalis {thoracic a) lynesi
Near Threatened. A. {t.) lynesi forms part of the
Bar-throated Apalis A. thoracica complex, which
has radiated into many different races in montane
eastern Africa. It is most closely related to the
yellow-bellied race {A. t. flavigularis ) of Zomba
and the Mulanje Mountains in adjacent Malawi
(Fig. 6). At Namuli, lynesi is very common in
forest and tall shrubland from 1,270-1,300 m
to at least 1,900 m. Some territories measured
on Muretha can be as small as 0. 3-0.6 ha
(forest plus some bracken scrub), but in three
patches of 1.0-1. 5 ha there was still just one
pair. Densities in continuous forest are probably
around five pairs/ 10 ha, and the population must
comprise at least 600-700 pairs, in 1,200-1,400
ha of forest, and probably more, as the species also
occupies narrow riparian strips and scrub forest
not included in this calculation. However, the
figure of a minimum of 5,000 pairs advanced by
Ryan et al. (1999a) appears excessive, and the size
of some territories given (0.02 ha) unrealistically
small. The smallest-ever occupied territories on
the Nyika (by Bar-throated Apalis) studied with
colour-ringed birds over three years are still 7-10
times larger than this (Dowsett-Lemaire 1983),
and the Namuli Apalises of Muretha appear more
widely spaced than their relatives on the Nyika.
Territorial limits were confirmed by using
playback of a pre-recorded tape from the Nyika
Plateau (race A. t.youngi). Pairs of Namuli Apalis
reacted strongly to the Nyika tape, coming to
within 1-2 m of the recorder, bill-snapping and
wing-clapping. The voice of the male sounds
identical between youngi and lynesi , but female
Namuli Apalis gives a faster titititititi, similar to
of A. t. flavigularis from Mulanje. One pair was
feeding young in a nest sited in a bush on the edge
of forest (23 November).
At Mabu the species is very rare and was found
only above 1,380-1,400 m: just one male was
heard in forest below the summit {c. 1,550 m),
and two males in forest above the second satellite
camp (c. 1,400 m), the more distant of which
appeared to be paired (female heard). Playback
at the upper edges of forest below the summit
elicited no response. Neither of the unmated
birds seemed interested in playback; one male
that was followed for >1 hour on 26-27 October
circulated over several hectares of forest with
many gaps, feeding at edges but also in the shaded
interior 1-3 m above the ground. The uneven
sex ratio suggests that conditions are suboptimal
for the species. Forms of Bar-throated Apalis
are usually very common in montane forest, but
locally in northern Malawi (as in the Misuku
Hills) the species can be uncommon, especially at
mid altitudes (Dowsett-Lemaire 1989). Possibly
a warm microclimate, combined with a tall
forest canopy, is not favourable for this montane
apalis, which prefers low-canopy forest and rich
shrubland. The population at Mabu must be very
small, with perhaps only a few dozen pairs.
White-winged Apalis Apalis chariessa
Vulnerable. A male was seen in riparian forest on
the Nanchili at 1,200 m, within a small mixed-
species party, on 27 November 2007. This species
avoids wetter types of mid-altitude forest, as in
adjacent Malawi it prefers edges and secondary
Albizia forest in the Shire Highlands to the wetter
Newtonia forests on Mount Mulanje (where
veiy rare, 1,000-1,300 m: Dowsett-Lemaire &
Dowsett 2006). This Eastern endemic, known
otherwise mainly from mid-altitude forest in
central Tanzania (Stuart & Jensen 1985, 1987),
reaches the southern limit of its range on Mount
Chiperone (Benson 1950, Spottiswoode et al.
2008). It must be very rare on Namuli (perhaps
too wet), and should be searched for in what is
left of the riparian forest on the drier side of the
mountain. However, given the rapid destruction of
this habitat the species is in danger ol extirpation.
It was not found on Mabu.
Playback often elicited vocal reactions from
Black-headed Apalis A. melanocephala , which is
common on both Mabu and Namuli. This may be
the result ol the superficial resemblance between
the piping motifs of these apalises, or due to
some form ol competition between these two
1 68 - Bull ABC Vol 17 No 2 (2010)
Ornithological exploration of Namuli and Mabu Mountains: Dowsett-Lemaire
canopy species. As reactions were obtained even
in Manho, where White-winged is veiy unlikely to
occur, the first hypothesis is preferred.
Dapple-throat Modulatrix orostruthus
Vulnerable. At Namuli confined to forest above
l, 500 or 1,600 m, up to 1,870 m in Ukalini
and Manho; one pair occupied two adjacent
patches on Muretha totalling 2.5 ha. Nothing
has been published on feeding behaviour (Keith
et al. 1992): individuals were seen feeding on the
ground, hopping and turning leaves like a thrush.
Sings low down, on small saplings, fallen logs or
just a hump on the ground. The alarm-call is a
striking modulated whistle, also given at the end
ol songs by birds counter-singing with neighbours
or reacting to playback. Individuals possess at least
2-3 song types (tape-recorded); the Tanzanian
populations produce slightly different motifs
(as on a tape from the Udzungwas, provided
by C. Carter), as is to be expected of distant
populations. The timbre and style of song are
strongly reminiscent of the melodious song of
another montane babbler, Grey-chested Illadopsis
Kakamega poliothorax, a remark also made by
B. Finch in Stevenson & Fanshawe (2002).
The species does not occupy the whole forest
as it is partial to areas with high densities of
saplings under a fairly closed canopy; it seems to
avoid Mimulopsis or other Acanthaceae thickets
(unlike Spot-throat M. stictigula elsewhere, as in
the Misuku Hills of northern Malawi, Dowsett-
Lemaire 1989). The population in Manho and
Ukalini could be 300-500 pairs, based on an
estimate of 3-5 pairs / 10 ha. Ryan et al.' s (1999a)
estimate of low thousands’ appears too high,
ignoring the fact that distribution is not uniform
in the large Manho Forest.
Its discovery on Mabu in 2008 represents a
small range extension, but the species is rare and
local, above 1,380 m. One tape-recorded near the
path to the summit at c. 1,500 m seemed strongly
territorial, while another sang that briefly near
our camp (1,400 m) was presumably a wanderer.
Only rwo territorial birds were found above the
second satellite camp, just below and at 1,400
m. One of these was followed for several hours
on 26-27 October, circulating over at least 5-6
ha, and was apparently paired. The bird’s scarcity
at Mabu is difficult to explain. It may be related,
in part, to the disturbance of the canopy and
unsuitable tangled understorey: this is striking
around the second satellite camp and is the result
of temporary human habitations used during
the civil war. As with Namuli Apalis, the overall
population could be quite small: a few dozen
pairs, perhaps up to 100, but further surveys are
necessary to verify this.
Green-headed Oriole Oriolus chlorocephalus
Fairly common at Mabu in the canopy and
subcanopy at 980-1,300 m, once at 1,400 m.
A wanderer in riparian forest was at 450 m; the
following day it was at c.400 m. The population of
this localised Eastern endemic must be important
at Mabu, which is reassuring given that part of
the small Malawi population was exterminated
through the deforestation of Thyolo Mountain. It
also occurs on Mount Chiperone (Benson 1950,
Spottiswoode et al. 2008).
Bertram’s Weaver Ploceus bertrandi
Very small numbers of this forest-edge species
were found on Namuli in 2007 (Demey 2007;
pers. obs.), including a pair at 1,580 m near a
nest from rhe previous year (suspended from
the frond of a Cyathea tree fern at a height of
2.5 m). One pair was seen by C. Spottiswoode
{in litt. 2009) at 920 m at the ecotone of forest
and Syzygium woodland at Mabu. This montane
endemic reaches the southern limit of its range on
Chiperone.
Green Twinspot Mandingoa nitidula
Very common at Mabu in forest and second
growth at 400-1,550 m. Scarce in most parts
of its range, it is exceptionally numerous here
with hundreds seen in a day near the tea house,
including many pairs and families coming to
drink in a small stream. Outside or on the edge of
forest it seemed to feed mainly on a small-seeded
Panicum. Inside forest it was found more at high
levels or in clearings, feeding on inflorescences
and small seeds of creepers. The species is also
locally common in southern Malawi, as in the
Shire Highlands and on Mulanje, where it occurs
to 1,550 m on the drier slopes. The reason why
it should become so scarce further west, as in
Zambia (Dowsett et al. 2008), is unknown.
Ornithological exploration of Namuli and Mabu Mountains: Dowsett-Lemaire
Bull ABC Vol 17 No 2 (2010) -169
Breeding activity
Over 50 breeding records were obtained on
Namuli in November 2007, for 20 species. Details
of these and earlier records can be found in
Dowsett-Lemaire (2008b). The breeding season
was much less advanced at Mabu in October, but
several species had started to lay or were feeding
young (see Dowsett-Lemaire & Dowsett 2009).
Bird densities at Namuli
Territory sizes of forest birds are easier to measure
in fragmented forest, and this was done on
Muretha Plateau: territory boundaries were
measured in three patches (of 1.0, 1.4 and 1.5
ha) over a period of 12 hours on two mornings,
and additional information on selected species
was obtained in a few other patches (0.5-1. 5
ha). Birds were very active in the early morning
and counter-singing between neighbouring pairs
was frequent. Playback was used in some cases to
confirm territorial boundaries, and the results are
shown in Table 1.
These figures compare well with those from
a three-year study of a large sample of birds of
the same or closely related species on the Nyika
Plateau, where most passerines were colour-ringed
and individually recognisable (Dowsett-Lemaire
1983). Territory sizes of Bar-throated Apalis
can be smaller (with usually two pairs / ha) and
densities of Eastern Mountain Greenbul on the
Nyika are twice as high, but this is in the absence
of its competitor the Stripe-cheeked (see above).
Table 1. Territory sizes of 14 bird species measured in small patches
(0.5, or 0.7 ha with bracken scrub, to 1.5 ha) on the Muretha Plateau.
Tableau 1. Dimension des territoires de 14 especes mesuree
dans des petites forets (0.5, ou 0.7 ha avec broussailles
adjacentes, et jusqu’a 1,5 ha) sur le Plateau de Muretha.
Species
Territory size Sample
Livingstone's Turaco Tauraco livingstonii
4-5 ha
2 pairs
Eastern Mountain Greenbul Andropadus nigriceps
1.0-1 .5 ha
4 pairs
Stripe-cheeked Greenbul Andropadus milanjensis
1.0-1. 5 ha
4 pairs
Cabanis’s Greenbul Phyiiastrephus cabanisi
1.0-1. 5 ha
4 pairs
White-starred Robin Pogonocichla stellata
0.7-1. 0 ha
5 pairs
Olive-flanked Robin Chat Cossypha anomala
1.0-1 .5 ha
4 pairs
Cholo Alethe Alethe choloensis
1.5 ha
1 unmated bird
Olive Thrush Turdus olivaceus
2.9 ha
1 unmated bird
Evergreen Forest Warbler Bradypterus iopezi
0.7-1. 5 ha
4 pairs
Namuli Apalis Apalis (thoracica) lynesi
0.7-1 .5 ha
4 pairs
Black-headed Apalis Apalis melanocephala
1.0-1 .5 ha
3 pairs
Cape (Malawi) Batis Batis capensis dimorpha
0.7-1 .0 ha
5 pairs
White-tailed Crested Flycatcher Elminia albonotata
1.0-1 .5 ha
3 pairs
Dapple-throat Modulatrix orostruthus
2.5 ha
1 pair
Otherwise, figures for other passerines are very
similar. For Schalow’s Turaco Tauraco schalowi ,
a close relative of Livingstone’s T. livingstonii, the
mean territory size is 4 ha, as 39 pairs were known
to occupy 43 forest patches totalling 1 57 ha. What
the Nyika study also showed is that, for most
species, territory sizes are smaller in fragmented
forest than in larger blocks, due to the edge effect
or inherent aggressive behaviour. Thus, it would
be wrong to transfer the densities observed on
Muretha to the larger Ukalini and Manho Forests.
Even if pairs of Namuli Apalises can occupy some
patches as small as 0. 5-0.7 ha, they will not
tolerate a neighbouring pair in patches of up to
1.5 ha, and it is unlikely that there would be more
than one pair in 2 ha of continuous forest. Apalises
spend much time feeding at sunny edges, as do
flycatchers (Cape Batis Batis capensis etc.) and
space themselves more in larger blocks of forest.
While White-chested Alethes Alethe fuelleborni on
the Nyika can breed in a patch as small as 0. 5-1.0
ha, when an ant colony moves in the overall
densities are low, e.g. two pairs in 8-10 ha forest
blocks, and a 25-ha portion of Chowo Forest
contained 5-6 pairs. (Incidentally Collar (2005)
wrote that Cholo Alethe could persist in a 'patch
as small as 0.5 ha so long as ant nest present’, but
there was confusion over the species involved as
this was never claimed for Cholo, but for White-
chested Alethe: Dowsett-Lemaire 1989).
Ryan et al. (1999a) counted birds at 72 points
for five minutes each and estimated the distance
at which the birds had been seen or heard (under
or over 20 m). They did this near the Nanchili
stream and in Ukalini Forest. The ‘two counting
band’ method of Bibby et al. (1992) was then used
to produce actual densities. The limitations and
assumptions of the method were not discussed
by Bibby et al. (1992). Ryan et al. (1999a: 321)
produced a table of densities for the commoner
18 species. Surprisingly, Olive-flanked Robin
Chat Cossypha anomala, one of the noisiest and
commonest birds on Namuli (including Ukalini),
is not listed. Figures for common small passerines
are of the order of 5-10 birds or pairs per ha (e.g.
12.6 in Namuli Apalis, 10.6 in Stripe-cheeked
Greenbul, 9.7 in White-tailed Crested Flycatcher
Elminia albonotata , 8.6 in Cholo Alethe, 8.4
in White-starred Robin, 2.4 in Dapple-throat
etc.). Even for a large non-passerine such as
1 70 - Bull ABC Vol 17 No 2 (2010)
Ornithological exploration of Namuli and Mabu Mountains: Dowsett-Lemaire
Livingstone s 1 uraco, they produced as many as
5.6 birds or pairs / ha.
Compared to territory sizes measured on
Muretha and in the Nyika study, these figures
are 5-30 times higher, depending on the species.
This suggests an inherent problem with the
methodology, evaluation of distances and also
probably with the formula used. This shows the
danger of relying on complicated calculations in
the absence of control against actual figures, and
led the authors to propose unrealistic figures of
overall numbers of threatened species, e.g. Cholo
Alethe {cf species account).
Biogeographical considerations
Table 2 shows the known distribution of
Alromontane bird species and selected Eastern
endemics on the five main massifs of the region,
from north to south, i.e. Namuli to Chiperone.
Thyolo Mountain has been included, despite
recent deforestation, because it had a unique
biogeographical and conservation value for several
threatened species: the forest covered c. 1 ,000 ha (in
one block) at 1,160-1,462 m until the mid 1990s.
Most records for Mount Chiperone come from
Benson (1950) and are based on a brief collecting
expedition by J. Makawa in July 1950, the rest
from Spottiswoode et al. (2008). The mention of
Cabanis’s Greenbul (race placidus) comes from a
specimen collected by J. Makawa (W. R. J. Dean
& R. Prys-Jones in lift. 2009) but missed from the
1950 publication. Chorographical status follows
Dowsett-Lemaire & Dowsett (2006).
The largest and tallest massif, Mulanje, has the
highest number of Afromontane species, 3 1 (if one
includes the sub-Afromontane Spotted Ground
Thrush), and Namuli comes a close second,
with 27 species. Only one species from Namuli
(Dapple-throat) is missing from Mulanje, and
Namuli Apalis is replaced by the flavigularis race of
Bar-throated; similarly, the montane Moustached
Green Tinkerbird on Mulanje is replaced by
the closely related Eastern Green Tinkerbird on
Namuli. Olive Bushshrike Malaconotus olivaceus
extends from southern Africa north to Mulanje,
Zomba and the Kirk Range (Dowsett-Lemaire
& Dowsett 2006) but does not reach Namuli.
The absence from Namuli of the remaining three
species can be explained in terms of habitat.
Striped Flufftail is almost certainly absent because
Table 2. Afromontane (near-)endemic and selected Eastern
endemic bird species present on Namuli, Mulanje, Thyolo, Mabu
and Chiperone Mountains. Most are forest birds, but NF (not
forest) after the species name indicates that the habitat consists
of grassland, rocks, montane shrubland or forest edges.
Tableau 2. Distribution des especes Afromontagnardes (endemiques
ou presque) et de certaines especes Orientales dans les massifs
de Namuli, Mulanje, Thyolo, Mabu et Chiperone. La plupart des
especes sont en foret, mais NF (pas en foret) apres le nom
de I'espece se refere a des milieux ouverts, prairies et milieux
arbustifs de montagne, zones rocheuses et lisieres forestieres.
Afromontane species
Striped Flufftail Sarothrura rufa (NF)
Rameron Pigeon Cotumba arquatrix
Lemon Dove Aplopelia larvata
Cape Eagle Owl Bubo capensis (NF)
Scarce Swift Schoutedenapus myoptilus
Bar-tailed Trogon Apaloderma vittatum
Moustached Green Tinkerbird Pogoniulus leucomystax
Blue Swallow Hirundo atrocaerulea (NF)
Grey Cuckooshrike Coracina caesia
Eastern Mountain Greenbul Andropadus nigriceps
Stripe-cheeked Greenbul Andropadus milanjensis
Cabanis’s Greenbul Phyllastrephus cabanisi
White-starred Robin Pogonocichla stellata
Swynnerton's Robin Swynnertonia swynnertoni
Olive-flanked Robin Chat Cossypha anomala
Cape Robin Chat Cossypha caffra (NF)
Cholo Alethe Alethe choloensis
Olive Thrush Turdus olivaceus
Orange Ground Thrush Zoothera gumeyi
Cinnamon Bracken Warbler
Bradypterus cinnamomeus (NF)
Evergreen Forest Warbler Bradypterus lopezi
Yellow-throated Warbler Phylloscopus ruficapilla
Wailing Cisticola Cisticola lais (NF)
Bar-throated Apalis Apalis thoracica
Namuli Apalis Apalis ( thoracica ) lynesi
Cape (Malawi) Batis Batis capensis dimorpha
White-tailed Crested Flycatcher Elminia albonotata
Dapple-throat Modulatrix orostruthus
Eastern Double-collared Sunbird Cinnyris mediocris
Olive Bushshrike Malaconotus olivaceus
Bertram's Weaver Ploceus bertrandi (NF)
Red-faced Crimsonwing Cryptospiza reichenovii
Swee Waxbill Estrilda melanotis (NF)
African Citril Serinus citrinelloides (NF)
Sub-Afromontane species
Spotted Ground Thrush Zoothera guttata
Selected Eastern species
Southern Banded Snake Eagle Circaetus fasciolatus
White-eared Barbet Stactolaema leucotis
Green Barbet Stactolaema olivacea
Eastern Green Tinkerbird Pogoniulus simplex
East Coast Akalat Sheppardia gunningi
White-winged Apalis Apalis charlessa
Green-headed Oriole Oriolus chlorocephalus
lx---
X X X X X
X X X X X
XX---
X X X - -
X X X X X
- X - - ?
- X - - -
- - X X X
XX---
X X X X X
X X X X X
X X X X X
- - - X -
X X - - X
XX-X-
X X X X X
X X X - X
X X X - X
- X - - -
X X X - X
X X X X X
XX-X-
-X---
X--X-
X X X X X
X X X - X
X- — X-
X X - - X
- X - - -
X X X X X
X X X - X
X X X X X
X X X - X
X X X X -
XXX
X - X
X - -
X -
X X
X -
- ?
- - - X -
X X X - X
- - X X X
Ornithological exploration of Namuli and Mabu Mountains: Dowsett-Lemaire
Bull ABC Vol 17 No 2 (2010) -171
of the nature of the grassland. Similarly there is
apparently no suitable habitat for Blue Swallow
Hirundo atrocaendea : the rocky or peaty nature of
the soils means that rain water immediately runs
off and fills every ditch, thus depriving the bird of
safe nest sites in the form of dry stream banks and
overhangs. An isolated population of Cinnamon
Bracken Warbler Bradypterus cinnamomeus
occurs in Mulanje’s extensive shrublands. On
Namuli second growth is much less extensive and
considerably impoverished floristically: thus, this
habitat is occupied by its congener, Evergreen
Forest Warbler B. lopezi. Many pairs were found
to extend their territories from forest into adjacent
bracken and scrub, an example of niche expansion
in the absence of competition.
The total number of Afromontane birds on
Mabu currently known is 18 species, and the
lower total is to be expected as there is hardly any
montane grassland or shrubland (hence species
like Blue Swallow cannot occur) and the areas
covered by Afromontane forest (as opposed to
mid-altitude forest) are relatively small. A few
high-altitude montane forest birds appear to be
absent (e.g. Olive-flanked Robin Chat, White-
tailed Crested Flycatcher, Eastern Double-collared
Sunbird Cinnyris mediocris ). The absence of
Evergreen Forest Warbler is more surprising as
it is common in mid-altitude forest in south-east
Malawi and reaches Mount Chiperone. In other
parts of Malawi, however, it can be rare in this
forest type (e.g. at Ntchisi). Even more surprising
is the apparent absence of Orange Thrush, as
this species is common in mid-altitude forest
elsewhere in the region. It is possible that further
exploration of the high-altitude sections of the
forest will reveal the presence of some additional,
discreet Afromontane species such as Red-faced
Crimsonwing Cryptospiza reichenoviv, the intra-
African migrant Scarce Swift could have been
missed for other reasons (see species account).
Within the Tanzania-Malawi group
Afromontane avifaunas are characterised by a
general impoverishment from north to south
(Dowsett-Lemaire 1989: 56, 80). Seven species
reach the southern limits of their ranges within
this region, all on Mount Chiperone (Bar-
tailed Trogon Apaloderma vittatum , Cabanis’s
Greenbul, Olive-flanked Robin Chat, Evergreen
Forest Warbler, Eastern Double-collared
Sunbird, Bertram’s Weaver and African Citril
Serinus citrinelloides ) as well as the race dimorpha
of Cape Batis, considered by some a separate
species. Cholo Alethe, endemic to the region, also
reaches Mount Chiperone. Moustached Green
Tinkerbird may not reach any further south than
Mulanje, but an unidentified green tinkerbird
(subgenus Viridibucco) was reported by Makawa
from Mount Chiperone (Benson 1950). In any
case Mulanje represents the southern limit for
Eastern Mountain Greenbul and Cinnamon
Bracken Warbler, while Dapple-throat, which
‘skips' Malawi altogether, reaches Mabu, a small
extension of range from Namuli.
A small cluster of species (Afromontane or
Eastern or otherwise) are shared between Thyolo,
Mabu and Chiperone: Eastern Bronze-naped
Pigeon, Grey Cuckooshrike and Green-headed
Oriole. They all reappear on Mount Gorongosa,
r.300-350 km to the south-west (Oatley &
Tinley 1989). Mount Chiperone remains under-
explored, especially the higher levels not reached
by Spottiswoode et al. (2008): in addition to
identifying the green tinkerbird, a form of Bar-
throated Apalis (the yellow-bellied race of Mulanje
or Namuli Apalis) should be sought in the
Afromontane forest there.
The presence of East Coast Akalat at
Mabu (up to 1,350 m) suggests that the local
microclimate is fairly warm. The distribution of
some lowland forest species on Mabu also supports
this assumption: Eastern Nicator Nicator gidar is,
Red-capped Robin Chat Cossypha natalensis and
Blue-mantled Flycatcher Trochocercus cyanomelas
all reach 1 ,400 m, whereas on the wet, southern
slopes of Mulanje they do not ascend above
800-950 m. On Namuli the nicator does not
ascend above 1,160 m (J. Graham in lift. 2008;
the qualification of this bulbul as being common
around 1,250 m in Ryan et al. 1999b was in error),
while Red-capped Robin Chat reaches 1,200 m
and the flycatcher has not been recorded (if it
occurs, it would be below 1,150 m). Similarly,
the warm microclimate of Mabu could explain
the scarcity of montane species such as Namuli
Apalis and Dapple-throat, whereas on Namuli
the apalis is already very common at 1,400-1,600
m. Even Cape Batis (with scattered pairs above
1,350-1,400 m) is much less common at Mabu
than on Namuli at a similar altitude.
172 -Bull ABC Vol 17 No 2 (2010)
Ornithological exploration of Namuli and Mabu Mountains: Dowsett-Lemaire
The conservation status of the Namuli and
Mabu forests
Namuli
Forest on the lower slopes of Mount Namuli
has been reduced by fires and localised logging
for decades. Vincent (1933) mentioned iron
smelting as an important activity in the area,
which would also have caused some forest losses.
The hunting of mammals throughout the massif
has been so intense that Bushpigs Potamochoerus
porcus (common in Vincent’s days) have totally
disappeared, to be replaced by domestic pigs. No
Klipspringer Oreotragus oreotragus or even Rock
Hyrax Procavia capensis are to be seen anywhere
on the granitic domes, which are occupied instead
by domestic goats. In 1932 Vincent’s base camp at
1,400 m was adjacent to ‘high forest’ or ‘primeval
forest’, where such species as Bar-tailed Trogon
and Green Barbet were collected; these could not
survive in the narrow riparian strips left today.
The lower limit of dense forest now is nearer
1,600 m. Aerial photos taken in 1969 show that
mid-altitude forest had already been reduced to
broad riparian strips. By 2007 numerous signs of
deforestation were visible far from the streams,
in the form of Harungana forest regrowth, or
scattered forest trees dying amid old fields.
Pressure on land from human settlements around
the foothills is increasing, and shifting cultivation
at 1,200-1,300 m has in places reached the very
edge of the Nanchili and Malema streams, causing
erosion. Ryan et al. (1999a) reported that there
was no forest encroachment above 1,500 m in
1998, but this is no longer true. A 5-ha fragment
of forest in Ukalini has been cleared at 1,580 m,
and there is a considerable problem of timber
extraction for planks (of Faurea wentzeliana) in
both Ukalini and Manho Forests. In Ukalini,
the number of felled Faurea is particularly high
and clearly unsustainable, creating many gaps in
the canopy. In Manho, two small areas of forest
at 1,700 m or just above were also clear-felled in
2007 to plant potatoes. A year later, in November
2008, the situation had worsened considerably as
there were many more sections of Manho Forest
cleared for gardens, some of them extensive (J.
Bayliss pers. comm. 2009). Potatoes are sold in
Gurue market and are grown more for cash than
for subsistence.
Some species of conservation concern that
occur at high densities at mid altitude must have
seriously declined due to deforestation at that
level, e.g. Cholo Alethe and, probably, Green
Barbet. White-winged Apalis, already very rare on
the southern slopes, has little chance of surviving
on Namuli. The fate of other threatened species
like Dapple-throat, Spotted Ground Thrush
and Namuli Apalis was of less concern until
recently, but the degradation of Manho Forest,
and the heavy logging of Faurea in Ukalini is very
worrying. Manho is the same size as the forest on
Thyolo Mountain in Malawi, most of which was
cleared by farmers in a period of five years.
Although not on the Red List, two high-
montane species occur on Namuli in (very) small
numbers, and need special attention. These are
Eastern Mountain Greenbul and especially Olive
Thrush, which are restricted to a few small patches
of high-altitude forest on Muretha and (the
greenbul) at the upper edges of Manho Forest.
One of the main threats to these may be climatic,
if indeed the climate is going to become warmer
or drier in the region, but in the more immediate
future these species are also very vulnerable to
any amount of disturbance through collecting.
Too many collecting expeditions from overseas
take no account of the small numbers of many
species in isolated montane forests; this has been
a serious problem in adjacent Malawi since the
early 2000s.
Mabu
The forest at Mabu is under much less pressure
than at Namuli. The human population in the
foothills is smaller and more scattered, and at
present shifting cultivation is practised entirely
within the woodland areas. The main damage
to the forest is in the form of dry-season bush
fires; the prolonged drought in October wrought
some real damage to forest edges at 800-1,000
m. Hunting for mammals or large birds is also
a problem, and has apparently led to the near-
extinction of Crested Guineafowl (as admitted
by the hunter interviewed). A large expanse
of lowland forest or transition woodland was
replaced by tea plantations at low levels but,
surprisingly, some forest understorey birds have
adapted to tea, especially East Coast Akalat and
Blue-mantled Flycatcher. It is possible that some
of the overgrown tea plantations will be replaced
Ornithological exploration of Namuli and Mabu Mountains: Dowsett-Lemaire
Bull ABC Vol 17 No 2 (2010) -173
by new crops, but there is no immediate plan for
this (J. Timberlake pers. comm. 2009), and the
low cost of tea makes renewed exploitation of tea
on a large scale unlikely.
Conclusion
The forests oi both Namuli and Mabu Mountains
are of extreme importance for the conservation of
several threatened and isolated bird species. The
forest at Mabu is considerably more extensive and
must now be considered a key area for the Cholo
Alethe, with a population at least equivalent in size
to that on Mount Mulanje in Malawi. Due to its
sheer size and remoteness, it must also be the most
important refuge for the belcheri race of Green
Barbet and several other species in the region,
above all East Coast Akalat and Swynnerton’s
Robin. But, as most of the forest is at mid altitudes
and the local microclimate appears relatively warm,
Dapple-throat and Namuli Apalis are found only
at the upper levels and in such low densities
that their survival in the long term may not be
guaranteed in the face of possible climate change.
For these two species alone, the conservation of
the Afromontane forest on Namuli must be a
priority. Further surveys are needed, in other high
sections of the forest at Mabu, and also on several
other peaks near Namuli that bear patches of
forest. Part of the Namuli plateau itself has yet to
be explored, especially the plateau c. 5 km south-
east of Ukalini, on the other side of the Malema
River; much of this plateau reaches c. 1,500 m
and is covered with forest patches. The forest
on Mount Chiperone, especially the upper levels
at 1,500-2,000 m, is still intact (J. Bayliss pers.
comm. 2008) and remains largely unexplored.
The Field Museum of Natural History (Chicago)
collected birds here at c. 1,600 m in late 2004,
but the results are unavailable (J. Bayliss & J.
Timberlake pers. comm. 2008-09).
The forests on Namuli and Mabu receive
no legal protection, and the Mozambique
government is yet to draft conservation legislation
for the country’s natural habitats. Any legal
dispositions likely to be taken should be combined
with agricultural projects aimed at helping local
communities, especially to improve the yield
of their crops closer to settlements. An agro-
industrial business operating in Mozambique was
at one stage interested in putting money into
conservation at Namuli, but unfortunately they
pulled out in 2009. Every effort should be made
to resurrect interest, as the situation at Namuli
requires urgent action.
Acknowledgements
I thank Jonathan Timberlake, Paul Smith and BirdLife
International for inviting me to undertake these surveys,
and the Darwin Initiative Award 15/036 and the
Tondation pour favoriser les recherches scientifiques
en Afrique’ (FFRSA, Brussels) for meeting my expenses.
Claire Spottiswoode kindly provided details of
unpublished observations at Mabu, as well as a copy of
the cassette of bird recordings made by Eric Herrmann
in December 2005 at Mabu and Thyolo. I am grateful
to Lincoln Fishpool for providing photographs of
Apalis warblers from the Natural History Museum
(Tring) and for comments on the text.
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requirements of montane forest birds on the Nyika
Plateau, south-central Africa. Gerfaut 73: 345-
378.
Dowsett-Lemaire, F. 1988. Fruit choice and seed
dissemination by birds and mammals in the
evergreen forests of upland Malawi. Rev. Ecol.
( Terre & Vie ) 43: 251-285.
Dowsett-Lemaire, F. 1989. Ecological and
biogeographical aspects of forest bird communities
in Malawi. Scopus 13: 1-80.
Dowsett-Lemaire, F. 2008a. On the singing habits
of forest honeyguides of the Guineo-Congolian
region, with a request for further information. Bull.
ABC 15: 24-35.
Dowsett-Lemaire, F. 2008b. Survey of birds on Namuli
Mountain (Mozambique), November 2007, with
notes on vegetation and mammals. Rep. for Darwin
Initiative Award 15/036. http://www.kew.org/
science/di rectory/ projects/an nex/namuli-birds-
Dowsett.pdf
Dowsett-Lemaire, L. & Dowsett, R. J. 2006. The Birds
of Malawi. Liege: Tauraco Press & Aves.
Dowsett-Lemaire, F. & Dowsett, R. J. 2009. The
avifauna and forest vegetation of Mt Mabu,
northern Mozambique, with notes on mammals.
Rep. for Darwin Initiative Award 15/036. Available
as a .pdf from the authors and from Kew, UK.
Fishpool, L. D. C. 2010. Brief notes on the birds of
Mount Inago, northern Mozambique. Bull. ABC
17: 198-201.
Gibbon, G. 1991. Southern African Bird Sounds. Six
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Hanmer, D. B. 1976. Birds of the Lower Zambezi.
Southern. Birds 2: 1-66.
Hockey, P. A. R., Dean, W. R. J. & Ryan, P. G. (eds.)
2005- Roberts — Birds of Southern Africa. Seventh
edn. Cape Town: )ohn Voelcker Bird Book Fund.
Irwin, M. P. S. 1981. The Birds of Zimbabwe. Salisbury
(Harare): Quest Publications.
Keith, S„ Urban, E. K. & Fry, C. H. (eds.) 1992. The
Birds of Africa. Vol. 4. London, UK: Academic
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Marsterson, A. N. B. & Child, G. F. T. 1959.
Ornithological notes on an expedition to the
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Melo, M. P., Covas, R. & Dijkstra, K.-D. undated
(c.2002). Namuli Massif, 1-6 December 2001.
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Oatley, T. B. & Tinley, K. L. 1989. The forest avifauna
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Parker, V. 1999. The Atlas of the Birds of Sul do
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Parker, V. 2001. Mozambique. In Fishpool, L. D. C.
& Evans, M. I. (eds.) Important Bird Areas in Africa
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Newbury: Pisces Publications & Cambridge, UK:
BirdLife International.
Parker, V. 2005. The Atlas of the Birds of Central
Mozambique. Cape Town: Avian Demography
Unit & Johannesburg: Endangered Wildlife Trust.
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V. & Spottiswoode, C. 1999a. The avifauna and
conservation status ol the Namuli Massif, northern
Mozambique. Bird Conserv. Intern. 9: 315-331.
Ryan, P., Spottiswoode, C., Parker, V., Graham,
J., Cohen, C. & Bento, C. 1999b. The birds of
Namuli, northern Mozambique: retracing Vincent’s
footsteps. Bull. ABC 6: 138-143.
Spottiswoode, C. N., Patel, I. H., Herrmann, E.,
Timberlake, J. & Bayliss, J. 2008. Threatened bird
species on two little-known mountains (Chiperone
and Mabu) in northern Mozambique. Ostrich 79:
1-7.
Stevenson, T. & Fanshawe, J. 2002. Field Guide to
the Birds of East Africa. London, UK: T. & A. D.
Poyser.
Stuart, S. N. & Jensen, F. P. 1985. The avifauna of
the Uluguru Mountains, Tanzania. Gerfaut 75:
155-197.
Stuart, S. N. & Jensen, F. P. 1987. Altitudinal zonation
of the avifauna in Mwanihana and Magombera
Forests, eastern Tanzania. Gerfaut7J: 165-186.
Vincent, J. 1933. The Namuli Mountains, Portuguese
East Africa. Geogr. J. 81: 314-332.
Vincent, J. 1933-36. The birds of Northern Portuguese
East Africa. Comprising a list of, and observations
on, the collections made during the British Museum
Expedition of 1931-32. Ibis (13)3: 611-652; 4:
126-160, 305-340, 495-527, 757-799; 5: 1-37,
355-397, 485-529, 707-762; 6: 48-125.
Le Pouget, 30440 Sumene, France. E-mail: dowsett@
aol.com
Received 23 October 2009; revision accepted 7 June
2010.
Ornithological exploration of Namuli and Mabu Mountains: Dowsett-Lemaire
Bull ABC Vol 17 No 2 (2010) -175
Appendix 1. Coordinates of main localities at
Namuli, Mabu and in the region.
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Annexe 1. Coordonnees des localites principales
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a Namuli, Mabu et dans la region.
Falconidae
Malawi'
Peregrine Falcon Falco peregrinus
R
H
F
Mount Mulanje (3,002 m)
Thyolo Mountain (1,462 m)
15°57'S 35°35’E
16°04’S 35°02'E
Phasianidae
Hildebrandt’s Francolin Francolinus hildebrandti
Red-necked Spurfowl Francolinus afer
FE/G
G
L/M/H
L
F
F
Mozambique:
Numididae
Mount Chiperone (2,054 m)
16°29’S 35°43'E
‘Crested Guineafowl Guttera pucherani (OK)
F
L
R
Namuli:
Columbidae
Namuli peak (2,419 m)
15°22’S 37°03'E
Rameron Pigeon Columba arquatrix
F
H
C
Muretha Plateau (1,860 m)
15°23’S 37°02'E
Eastern Bronze-naped Pigeon Columba delegorguei
F
M
C
Malema River bridge (1,250 m)
15°24’S 37°04’E
Lemon Dove Aplopelia larvata
F
H
C
Mabu :
Blue-spotted Wood Dove Turturafer
F/W
L
F
Mabu peak (1,710 m)
16°18’S 36°24’E
Tambourine Dove Turturtympanistria
F
L/M/H
C
Main forest camp (980 m)
16°17’S 36°24’E
Psittacidae
Camp at tea house (540 m)
16018’S 36°25’E
‘Brown-necked Parrot Poicephalus robustus (OK)
F/W
L/M/H
u
Musophagidae
Livingstone’s Turaco Tauraco livingstonii
F
L/M/H
c
Appendix 2. Bird species recorded at Mabu.
Species marked * were noted by other observers, followed by their initials: CS
(C. Spottiswoode in December 2005), LF (L. D. C. Fishpool), MC (M. Curran), OK
(hunter Ofelio Kavaliyawo). Habitats: F = forest; FE = forest edge; W - transition
woodland; G = grassland and scrub; R = granitic dome; FI - commensal (tea
house). Altitudinal limits: L = 400-1,000 m; M = 1,000-1,400 m; H = c.1,400 m
and above. Status: C = common (recorded daily in relevant habitat); F = fairly
frequent; U = few records; R = rare or vagrant. Dates of Palearctic migrants
appear in brackets after name.
Annexe 2. Liste des especes observees a Mabu.
Les especes marquees d'un asterisque ont ete notees par d’autres observateurs,
dont les initiales suivent : CS (C. Spottiwoode en decembre 2005), LF (L. D.
C. Fishpool), MC (M. Curran), OK (Ofelio Kavaliyawo). Habitats : F = foret
dense ; FE = lisieres forestieres ; W = foret claire de transition ; G = formation
herbeuse et arbustive ; R = dome granitique ; FI = milieu commensal (batiments).
Limites altitudinales : L = 400-1.000 m ; M = 1.000-1.400 m ; H = c.1.400 m et
au-dessus. Statut : C = commun (note tous les jours dans le milieu approprie) ;
F = assez frequent ; U = peu de donnees ; R = rare ou accidentel. Les dates de
migrateurs palearctiques apparaissent entre parentheses apres le nom.
Accipitridae
African Cuckoo Hawk Aviceda cuculoides F/W
European Honey Buzzard Pernis apivorus (19 Oct, ‘Dec, CS) F
Palm-nut Vulture Gypohierax angolensis F
Brown Snake Eagle Circaetus cinereus F/W
Southern Banded Snake Eagle Circaetus fasciotatus F/W
African Harrier Hawk Polyboroides typus F/W
African Goshawk Accipiter tachiro F
Lizard Buzzard Kaupifalco monogrammicus W
Common Buzzard Buteo buteo (30 Oct, ‘Dec, CS) W
‘Augur Buzzard Buteo augur (LF) W
Lesser Spotted Eagle Aquila pomarina (23 Oct) F/R
Ayres's Hawk Eagle Hieraaetus ayresii F/W
Crowned Eagle Stephanoaetus coronatus F
L R
L R
H R
L F
L/M/H F
L/M/H F
L/M/H C
L R
L R
L R
H R
L U
M/H C
Cuculidae
Red-chested Cuckoo Cuculus solitarius
African Emerald Cuckoo Chrysococcyx cupreus
Klaas’s Cuckoo Chrysococcyx klaas
Yellowbill Ceuthmochares aereus
Burchell’s Coucal Centropus superciliosus
Tytonidae
Barn Owl Tyto alba
Strigidae
Spotted Eagle Owl Bubo africanus
African Wood Owl Strix woodfordii
Apodidae
African Palm Swift Cypsiurus parvus
Common Swift Apus apus (29 Oct)
White-rumped Swift Apus caffer
Mottled Swift Tachymarptis aequatorialis
Alpine Swift Tachymarptis melba
Trogonidae
Narina’s Trogon Apaioderma narina
Bar-tailed Trogon Apaioderma vittatum
Alcedinidae
African Pygmy Kingfisher Ceyx plctus
Grey-headed Kingfisher Halcyon leucocephala
Meropidae
Little Bee-eater Merops pusillus
Madagascar Bee-eater Merops superciliosus
Eurasian Bee-eater Merops apiaster (11-28 Oct)
Coraciidae
Broad-billed Roller Eurystomus glaucurus
Bucerotidae
Crowned Hornbill Tockus alboterminatus
Silvery-cheeked Hornbill Bycanistes brevis
Lybiidae
White-eared Barbet Stactolaema leucotis
Green Barbet Stactolaema olivacea
Yellow-rumped Tinkerbird Pogoniulus bilineatus
Indicatoridae
Scaly-throated Honeyguide Indicator variegatus
Lesser Honeyguide Indicator minor
F/W L R
F L R
F/W L F
F L R
FE/G L/M C
W/H L U
W/R L U
F L/M/H C
W L U
W L R
W/H L U
R L/H F
R H U
F L/M C
F H C
FE L F
W L R
G L R
W L U
F/W L/M/H F
W L U
F/W L U
F L/M/H C
F L/M U
F L/M/H C
F/W L/M/H C
F/W L/M F
F L U
176 -Bull ABC Vol 17 No 2 (2010)
Ornithological exploration of Namuli and Mabu Mountains: Dowsett-Lemaire
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Pallid Honeyguide Indicator meliphilus
F
L/M
u
Muscicapidae
Picidae
'Spotted Flycatcher Muscicapa striata (CS, 11 Dec)
w
L
u
Golden-tailed Woodpecker Campethera abingoni
F
M/H
u
Ashy Flycatcher Muscicapa caerulescens
W/FE
L
c
Cardinal Woodpecker Dendropicos fuscescens
W/F
L
u
Lead-coloured Flycatcher Myioparus plumbeus
W/F
L/M
F
Eurylaimidae
Platyteiridae
African Broadbill Smithornis capensis
F
L
F
Cape (Malawi) Batis Batis capensis dimorpha
F
H
U
Hirundinidae
Mozambique Batis Batis soror
W/FE
L/M
F
Black Saw-wing Psalidoprocne pristoptera
FE
L/M
F
Monarchidae
Lesser Striped Swallow Cecropis abyssinica
W/H
L
F
Blue-mantled Flycatcher Trochocercus cyanomelas
F
L/M
C
Barn Swallow Hirundo rustica (from 23 Oct)
W/F
L/M/H
F
African Paradise Flycatcher Terpsiphone viridis
F
M
U
Eurasian House Martin Delichon urbicum (28-29 Oct)
R/W
L/H
F
Timaliidae
Motacillidae
Dapple-throat Modulatrix orostruthus
F
H
R
‘Mountain Wagtail Motacilla clara (MC)
R/F
L
U
Paridae
Striped Pipit Anthus lineivenths
R/G
H
U
Rufous-bellied Tit Pams rufivenths
W
L
R
Campephagidae
Nectariniidae
Grey Cuckooshrike Coracina caesia
F
M
F
Violet-backed Sunbird Anthreptes longuemarei
F
L
R
Pycnonotidae
Collared Sunbird Hedydipna collaris
F
L
C
Stripe-cheeked Greenbul Andropadus milanjensis
F
M/H
C
Olive Sunbird Cyanomitra olivacea
F
L/M/H
C
Little Greenbul Andropadus wens
F
L/M/H
C
Amethyst Sunbird Chalcomitra amethystina
W
L
F
'Yellow-bellied Greenbul Chlorocichla flaviventris (CS)
F
L
u
Yellow-bellied Sunbird Cinnyris venustus
W,G
L/H
F
Grey-olive Greenbul Phyllastrephus cerviniventris
F
L
F
Zosteropidae
Cabanis’s Greenbul Phyllastrephus cabanisl
F
L/M/H
C
Yellow White-eye Zosterops senegalensis
F/W
L/M/H
C
Yellow-streaked Greenbul Phyllastrephus flavostriatus
F
L/M/H
c
Oriolidae
Common Bulbul Pycnonotus barbatus
W/FE
L/M/H
c
Green-headed Oriole Oriolus chlorocephalus
F
(L)/M
C
Eastern Nicator Nicator gularis
F
L/M
c
Malaconotidae
Turdidae
Black-fronted Bushshrike Malaconotus nigrifrons
F
M
c
White-starred Robin Pogonocichla stellata
F
H
c
Brown-headed Tchagra Tchagra australis
G/W
L
F
Swynnerton's Robin Swynnertonia swynnertoni
F
H
F
Southern Puffback Dryoscopus cubla
W/F
L/M
c
East Coast Akalat Sheppardia gunning i
F
L/M
C
Tropical Boubou Laniarius aethiopicus
FE/G
L/M/H
F
Cape Robin Chat Cossypha caffra
G/FE
H
F
Dicruridae
Red-capped Robin Chat Cossypha natalensis
F
L/H
C
Square-tailed Drongo Dicrurus ludwigii
F
L/M
C
Eastern Bearded Scrub Robin Cercotrichas quadrivirgata
F
L
C
Corvidae
White-browed Scrub Robin Cercotrichas leucophrys
W
L
U
White-necked Raven Corns albicollis
R/W
L/M/H
F
Cholo Alethe Alethe choloensis
F
M/H
C
QturnidflP
Spotted Ground Thrush Zoothera guttata
Kurrichane Thrush Turdus libonyanus
F
W
M
L
R
R
oiui i iiuac
Red-winged Starling Onychognathus morio
Ploceidae
R/FE
M/H
U
Sylviidae
W/FE
L
F
'Bertram’s Weaver Ploceus bertrandi (CS)
FE/W
L
R
Red-faced Crombec Sylvietta whytii
Spectacled Weaver Ploceus ocularis
FE
L
U
Yellow-throated Warbler Phylloscopus ruficapilla
F
M/H
C
Dark-backed Weaver Ploceus bicolor
F
L/M/H
C
Garden Warbler Sylvia borin (30 Oct)
F
L
R
'Grosbeak Weaver Amblyospiza albifrons (CS)
FE
L
R
Cisticolidae
G/R
H
L
Estrildidae
Wailing Cisticola Cisticola lais
C
Green Twinspot Mandingoa nitidula
F/FE
L/M/H
C
Red-faced Cisticola Cisticola erythrops
G
F
Blue-billed Firefinch Lagonosticta rubricata
FE
L
U
Tawny-flanked Prinia Prinia subflava
G
L
F
Swee Waxbill Estrilda melanotis
RIG
H
R
Red-winged Warbler Heliolais erythropterus
G
L
U
Common Waxbill Estrilda astrild
G
L
C
Yellow-breasted Apalis Apalis flavida
F
L
F
Bronze Mannikin Spermestes cucullatus
G
L
C
Namuli Apalis Apalis (thoracica) lynesi
F
H
R
Red-backed Mannikin Spermestes bicolor
FE/W
L
C
1 Black-headed Apalis Apalis melanocephala
F
L/M/H
C
Fringillidae
Yellow-fronted Canary Serinus mozambicus
Grey-backed Camaroptera Camaroptera brachyura
W/F
L/M
C
G/W
L
F
Ornithological exploration ofNamuli and Mabu Mountains. Dowsett-Lemaiu
Bull ABC Vol 17 No 2 (2010) -177
The sweet option: the importance of Aloe marlothii for
opportunistic avian nectarivores
Craig Symes
L’option douce : l’importance de Aloe marlothii pour des nectarivores aviens opportunistes. Les
especes de Aloe sont endemiques a l’Airique, oil elles sont repandues, offranr du nectar a une multitude
d’especes animales. Cet article resume les resultats d une etude de trois ans, menee dans la Reserve naturelle
du Suikerbosrand, Gauteng, Afrique du Sud, qui avait pour objectif d’examiner l’importance du nectar de
A. marlothii pour les oiseaux. Le nectar est dilue et copieux et facilement accessible pour une multitude de
nectarivores opportunistes (au moins 77 especes) qui agissent comme pollinisateurs legitimes.
Summary. Aloe species are endemic and widespread in Africa, offering nectar to a host of animal species.
This paper summarises the findings of a three-year study at Suikerbosrand Nature Reserve, South Africa,
investigating the importance of A. marlothii nectar for birds. The nectar is dilute and copious and easily
accessible to a host of opportunistic neactarivores (at least 77 species) that act as legitimate pollinators.
loe Linnaeus, species are widespread in the
Afrotropical region with a concentration
of diversity in southern Africa (Holland 1978,
Reynolds 1969, Glen & Hardy 2000, Van Wyk
& Smith 2005). A uniquely charismatic and
widespread species found in South African savannas
is Aloe marlothii A. Berger (Asphodelaceae), a
single-stemmed aloe that grows up to 6 m in height
(Reynolds 1969, Glen & Hardy 2000, Van Wyk
& Smith 2005). Flowers vary in colour throughout
their range from bright orange to red, and gaudy
infloresences suggest pollination by birds (Reynolds
1969, Glen & Hardy 2000, Van Wyk & Smith
2005). The dilute nectar (c. 12%), produced in
copious amounts (c.250 pl/flower) during the dry
winter period (June-September), when little else
is flowering, attracts a host of opportunistic avian
nectarivores (Symes & Nicolson 2008, Symes et
al. 2008). Herein I summarise aspects of a three-
year study investigating the symbiotic relationship
of A. marlothii and a suite of avian opportunistic
nectarivores.
An Aloe marlothii nectar oasis for birds
The first comprehensive documentation of birds
feeding on A. marlothii nectar was by Oatley ( 1 964)
at Ndumu Game Reserve in northern KwaZulu-
Natal. His list included 43 nectar-feeding bird
species belonging to 21 families. Although earlier
accounts exist (Marloth 1915), very little work has
been done in understanding these animal-plant
interactions. This prompted a study at a large
aloe ‘forest’ at Suikerbosrand Nature Reserve,
c.60 km south-east of Johannesburg, where large
numbers of plants grow on rocky, north-facing
slopes. During transects over six months almost
half (38 of 83 species) of all species detected
were recorded feeding on nectar (Symes et al.
2008). An additional four species were recorded
feeding on nectar outside of transects (Symes et
al. 2008). In most observations, birds were seen
probing the compact arrangement of flowers on
the near-horizontal racemes. However, for many
birds the bright wash of orange pollen dusted on
the facial area and belly was sufficient evidence for
a nectar ‘addiction’ (Fig. 1). Overall, throughout
the range of A. marlothii , at least 77 bird species
are known to feed on the plant’s nectar. Although
most of the species observed feeding on nectar
were residents, some species only appeared when
nectar was available during flowering. During this
period bird diversity and abundance increased
significantly, suggesting that their arrival is
dictated by the availability of the sugar-rich nectar
of A. marlothii. One species that arrived in large
numbers when A. marlothii flowered was Wattled
Starling Creatophora cinerea. Most starlings
(Sturnidae), mockingbirds (Mimidae), thrushes
(Turdidae) and robins (Muscicapidae) are unable
to digest sucrose, a Cl 2 sugar comprising two C6
sugars, glucose and fructose (Martinez del Rio &
Stevens 1989, Martinez del Rio et al. 1992, Lotz
& Schondube 2006). However, most aloe nectars
are glucose/lructose dominated (van Wyk et al.
1993) making their nectars suitable for a wider
range of bird species.
Sunbird abundance during the flowering
period at Suikerbosrand was notably low and
178 - Bull ABC Vol 17 No 2 (2010)
Importance of Aloe marlothii for opportunistic avian nectarivores: Symes
could be explained by nectar characteristics.
Recent studies of plant— pollinator relationships
suggest that nectar concentration and volume are
important predictors of pollination syndromes,
with nectars of high volume (40-100 pl/flower)
and low concentration (8-12% w/w) focused
towards generalist pollinators, and nectars of low
volume (10-30 pl/flower) and high concentration
(15-23% w/w) attracting specialist nectarivores
e.g., sunbirds (Johnson & Nicolson 2008).
However, in the Eastern Cape the response of
birds to winter-flowering A. ferox might be quite
different. Although the nectar in this ecologically
similar aloe is of similar concentration and volume
(180 pi, 12.5% w/w) it attracts large numbers
of Malachite Sunbird Nectarinia famosa so other
factors (like a lack of major foodplants at this
season) besides nectar characteristics could be
important determinants of plant visitors.
The natural world is an incredible assemblage
of symbiotic relationships. Birds eat nectar but
how do aloes benefit? By feeding in a manner
where pollen is deposited onto feathers, generalist
birds act as important pollinators of A. marlothii.
This was confirmed during two flowering seasons
by conducting pollinator exclusion experiments
(Symes et al. 2009). Honeybees Apis mellifera
also visited aloes but in smaller numbers; they
are probably excluded as pollinators because the
nectar is more dilute than they prefer and because
they were present in such low numbers at this
specific site; where numbers are greater their role
as pollinators might be more important.
The tubular length of A. marlothii flowers
(c.33 mm) suggests a specialist bird-pollinated
syndrome (i.e. sunbirds). However, because large
amounts of nectar ooze from the flower opening,
many short-billed birds can access the nectar
without damaging flowers. No birds have been
observed (like Cape White-eye Zosterops capensis )
robbing nectar, confirming the legitimacy of most
visitors as true pollinators.
Of particular importance to the study was the
use of stable isotopes, a technique that was in its
infancy in the 1960s when Terry Oatley made
his observations of opportunistic nectarivory at
A. marlothii. Stable carbon isotopes are a useful
tool in understanding animal diets because they
quantify assimilated material, and depending on
the tissue studied (which is related to turnover
rates of tissue) provide a window into different
dietary time periods. A. marlothii employs a
unique water-saving carbon fixation pathway
during photosynthesis (i.e. crassulacean acid
metabolism or CAM photosynthesis), which is
found in many plants of arid regions. Because
of this, it has a unique carbon isotopic signature
compared to C photosynthesising plants. By
measuring the carbon isotopic signature (SI3C) in
whole blood before, during and after flowering,
I was able to track the dietary shift of birds from
that of a C, photosynthetic source (i.e. broad-
leaved plants) to nectar (with a CAM isotope
signature). Furthermore, by measuring carbon
isotope signatures of CO, in breath samples 1 was
able to determine the importance of nectar sugars
as a readily available energy source for birds; this
is because carbon in breath represents immediately
metabolised carbohydrates (Symes et al. in prep.).
The analysis of breath also indicated that analysis
of blood under-estimated the importance of nectar
sugars for most nectar-feeding birds.
Table 1 . Number of extant species in dominant nectarivore families for each zoogeographic region (shaded), including sunbirds
(Nectariniidae), sugarbirds (Promeropidae), honeyeaters (Meliphagidae) and hummingbirds (Trochilidae) (after Maclean 1990).
Tableau 1 . Nombre d’especes dans les families essentiellement nectarivores pour chaque region zoogeographique (hachure) :
souimangas (Nectariniidae), promerops (Promeropidae), meliphages (Meliphagidae) et colibris (Trochilidae) (d'apres Maclean 1990),
Neotropics
Nearctic
Palaearctic
Afrotropics
Indo-Malaya
Australasia
Total
Trochilidae
324
13
0
0
0
0
337
Nectariniidae
0
0
2
78
39
2
121
Promeropidae
0
0
0
2
0
0
2
Meliphagidae
0
0
0
0
10
159
169
324
13
2
80
49
161
629
Importance of Aloe marlothii for opportunistic avian nectarivores: Symes
Bull ABC Vol 17 No 2 (2010) - 179
Figure 1. African Red-eyed Bulbuls Pycnonotus nigricans
feeding on Aloe marlothii flowers. The study site formed
a region of overlap with Dark-capped Bulbul Pycnonotus
tricolor (which were never observed, although hybrids
were) (Craig Symes)
Bulbuls brunoirs Pycnonotus nigricans se nourrissant sur les
fleurs de Aloe marlothii. Le site d’etude formait une zone
de chevauchement avec le Bulbul des jardins Pycnonotus
barbatus tricolor (qui n’a jamais ete observe, bien que des
hybrides ont ete vus) (Craig Symes)
Figure 2. Avian nectar feeders in Aloe marlothii forest
at Suikerbosrand Nature Reserve, Gauteng (a-f) and
common avian pollinators showing pollen dusted on facial
area from feeding on nectar (g-j).
(a) Immature male Malachite Sunbird Nectarinia famosa
and African Red-eyed Bulbul Pycnonotus nigricans; (b)
Aloe marlothii inflorescences; (c) Cape White-eye Zosterops
capensis; (d) immature male Malachite Sunbird Nectarinia
famosa probing flowers on raceme; (e) Wattled Starling
Creatophora cinerea\ (f) inflorescence with Fiscal Flycatcher
Sigelus silens perched on open flowers; (g) adult male Cape
Weaver Ploceus capensis; (h) Black-collared Barbet Lybius
torquatus; (i) female Wattled Starling Creatophora cinerea;
(j) Red-faced Mousebird Urocolius indicus (Craig Symes)
Oiseaux se nourrissant de nectar dans une foret de Aloe
marlothii, Reserve naturelle du Suikerbosrand, Gauteng,
Afrique du Sud (a-f) et pollinisateurs aviens communs
avec du pollen sur leur face OK apres avoir pris du nectar
(g-j)-
(a) Souimanga malachite Nectarinia famosa male immature
et Bulbul brunoir Pycnonotus nigricans ; (b) inflorescences
de Aloe marlothii ; (c) Zosterops du Cap Zosterops capensis ;
(d) Souimanga malachite male immature explorant des
fleurs ; (e) Etourneau caroncule Creatophora cinerea ; (f)
inflorescence avec un Gobemouche fiscal Sigelus silens
perche sur des fleurs ouvertes ; (g) Tisserin du Cap
Ploceus capensis male adulte ; (h) Barbican a collier Lybius
torquatus ; (i) Etourneau caroncule Creatophora cinerea
femelle ; (j) Coliou quiriva Urocolius indicus (Craig Symes)
1 80 - Bull ABC Vol 17 No 2 (2010)
Importance of Aloe marlothii for opportunistic avian nectarivores: Symes
Importance of Aloe marlothii for opportunistic avian nectarivores: Symes
Bull ABC Vol 17 No 2 (2010) -181
Avian nectarivory in the Afrotropics
Avian nectarivory is most broadly dominated by
three families: the New World hummingbirds
(Trochilidae), the Old World sunbirds
(Nectariniidae)andtheAustralo-Pacifichoneyeaters
(Meliphagidae) (Maclean 1990; Table 1). The
sugarbirds (Promeropidae, two species) were once
considered a unique nectar-feeding family of
Africa, although a recent study suggests additions to
this taxon (i.e. Grey-chested Illadopsis Kakamega
poliothorax , Spot-throat Modulatrix stictigula
and Dapple-throat Arcanator orostruthus ) that
are not nectar feeders (Beresford et al. 2005).
Nectar-feeding is not confined to specialist taxa
and occurs in a wide range of other families.
In the Neotropics the number of nectar-feeding
specialists, besides hummingbirds, is comparatively
low and includes members of the Dacnini and
Coerebini, tribes of the Thraupidae and Parulidae
respectively (Burns et al. 2003, Dickinson 2003).
In some regions where these major nectarivore
families have not colonised, and monopolised
the nectar-feeding niche, diversification within
other families has occurred (Nicolson & Fleming
2003). These include, for example, the Hawaiian
honeycreepers (Drepanidinae) (Pratt 2005), the
asities and sunbird-asities (Philepittidae; four
species) of Madagascar (Prum 1993, Irestedt
et al. 2001), the Irenidae (fairy-bluebirds; two
species), Chloropseidae (leafbirds; eight species)
and Aegithinidae (ioras; four species) of the Indo-
Malayan Region (Wells et al. 2003a, Dickinson
2003, Fuchs et al. 2006), and the Dicaeidae
(flowerpeckers, 42 species) of Australasia (Delacour
1944, Beecher 1953, Sibley & Ahlquist, 1991,
Ericson & Johansson 2003). The enigmatic
Lorinae (Psittacidae) of Australasia are also
uniquely adapted for nectarivory with a brush-tip
tongue (Forshaw 2006), as is a single member of
the Timalidae (babblers), the Fire-tailed Myzornis
Myzornis pyrrhoura (Wells et al. 2003b). However,
the Melanocharitidae (berrypeckers, 12 species)
of New Guinea lack the specialised structure
of the tongue for feeding on nectar (Beehler
et al. 1986). The stitchbird (Notiomystidae),
recently relegated to a monotypic family (from
Meliphagidae), is a nectar-feeder endemic to New
Zealand (Driskel et al. 2007).
In the Afrotropics the overall diversity of
opportunistic nectar-feeding birds is unknown.
This study has highlighted the high diversity
of opportunistic nectar feeders for a single aloe
species in southern Africa. Therefore, for the rest
of the continent this list could be greatly increased.
To date the diversity of opportunistic nectarivores
appears greater than in other zoogeographic
regions, and is probably explained by the different
feeding roles of birds in different regions. In
the Australo-Pacific region the equivalent role
of opportunistic nectarivores might be filled by
honeyeaters with broader dietary requirements,
whilst in the Afrotropics the role of opportunistic
nectarivores may be filled by several families
that do not typically feed on nectar (Keast
1985; Appendix). Furthermore, competition
of opportunistic nectarivores with specialist
nectarivores (i.e. sunbirds) in the Afrotropics could
be high, thereby explaining the low number of
sunbird species in the Afrotropics compared to the
number of hummingbird and honeyeater species
in the Neotropics and Australasia respectively,
where there are fewer opportunistic nectarivores
(Table 1). An alternative explanation may relate
to degrees of weather predictability and associated
plant assemblages and flowering patterns in each
of the regions.
Other interactions involving aloes
Aloe marlothii nectar is important for many other
organisms besides birds and the use of nectar
might be an important determinant of local
movements for Chacma Baboons Papio hamadryas
ursinus. Observations suggest that troops with
ranges that overlap with A. marlothii make greater
use of the aloe forest during flowering, utilising
nectar and succulent leaves as a food and water
source (pers. obs.). During periods of low rainfall
other mammal species might make use of Aloe
nectar but may occur in such low numbers that
the scale of competition with birds is low.
Aloe marlothii is also important to birds for
many other reasons. The most abundant bird
species recorded during censuses was Laughing
Dove Streptopelia senegalensis, a species that
seldom (if ever) fed on nectar. It was observed
nesting during drier months (August-September)
on horizontal leaves of tall aloes. Although the
spines of aloes afford protection from predators,
baboons are able to ascend plants to access nectar
or rob nests. Also, avian predators might still pose
a threat; in one instance a Pied Crow Corpus alhus
was recorded robbing a nest with eggs (pers. obs.);
182 -Bull ABC Vol 17 No 2 (2010)
Importance of Aloe marlothii for opportunistic avian nectarivores: Symes
the latter species was, however, never observed
feeding on nectar. Aloes also benefited birds
in other ways besides providing nectar. Water
collected after rains in the horizontal leaves was
used as a drinking and bathing source by birds.
Barbets excavated nesting cavities in trunks of
tall aloes, and the dry leaf skirt was used as a
protected site for birds to construct nests (e.g.
Fiscal Flycatcher Sigelus si lens).
Conclusion
The list of birds recorded feeding on aloes has
increased from that previously known and includes
at least 101 species in 26 families (Appendix).
Some species might irregularly feed on nectar
and observations of them doing so might be rare:
A. marlothii is a widespread species in southern
Africa and the number of species feeding on its
nectar could therefore exceed 77 species. This
phenomenal diversity of opportunistic nectarivores
is possibly the highest number of bird species
recorded feeding on the nectar of a single plant
species worldwide (Appendix 1).
Acknowledgements
This study was funded by the National Research
Foundation (South Africa). Darren Pietersen and
Tracy Symes are thanked for assistance with the field
work. Franqoise Dowsett-Lemaire commented on the
submitted manuscript.
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Received 3 December 2008; revision accepted 21
September 2009.
Appendix 1 . Bird species recorded feeding on, or suspected of feeding on, Aloe marlothii nectar.
Dominant feeding guild (after Maclean 1993): fr = frugivore, gr = granivore, in = insectivore, ne = nectarivore, om = omnivore.
Level of nectarivory (after Oatley 1964): 0 = non-feeder but present therefore suspected feeder, 1 = occasional, 2 = casual, 3 = regular, 4 = addict, 5 = true nectarivore.
SNR = recorded at Suikerbosrand Nature Reserve.
References: 1 = Oatley (1964), 2 = Skead (1967), 3 = Oatley & Skead (1972), 4 = Hoffman (1988) (records attributed to A. ferox ), 5 = Maclean (1993), 6 = Oatley (2001),
7 = pers. obs„ 8 = this study, 9 = A. Craig pers. comm, (records attributed to A . ferox), 10 = B. de Boer pers. comm., 11 = M. Kriek pers. comm., 12 = C. Botes unpubl.
data. Taxonomy follows Hockey et a/. (2005).
* Buphagus erythrorhynchus was observed for the first time at the study site (first known record for SNR) only during the flowering period and is by association with A.
marlothii recorded as a nectar feeder.
Annexe 1 . Especes d'oiseaux ayant ete observees en train de se nourrir du nectar de Aloe marlothii ou suspectees de le faire.
Regime alimentaire dominant (d’apres Maclean 1993) : fr = frugivore, gr = granivore, in = insectivore, ne = nectarivore, om = omnivore.
Niveau de nectivorie (d’apres Oatley 1964) : 0 = n’a pas ete observe se nourrissant de nectar mais present et ainsi suspecte de le faire, 1 = accidentel, 2 = occasionnel, 3
= regulier, 4 = tres regulier, 5 = vrai nectarivore.
SNR = observe dans la Reserve naturelle du Suikerbosrand.
References : 1 = Oatley (1964), 2 = Skead (1967), 3 = Oatley & Skead (1972), 4 = Hoffman (1988) (mentions attribuees a A. ferox), 5 = Maclean (1993), 6 = Oatley
(2001), 7 = obs. pers., 8 = cette etude, 9 = A. Craig comm. pers. (mentions attribuees a A. ferox), 10 = B. de Boer comm, pers., 11 = M. Kriek comm, pers., 12 = C. Botes
donnees non publiees. La taxonomie suit Hockey et al. (2005).
* Buphagus erythrorhynchus a ete observe pour la premiere fois sur le site d’etude (premiere mention connue pour SNR) uniquement pendant la periode de floraison et
est considere comme un nectarivore par son association avec A. marlothii.
184 - Bull ABC Vol 17 No 2 (2010)
Importance of Aloe marlothii for opportunistic avian nectarivores: Symes
Feeding Guild Level of nectarivory
Species and family
Indicatoridae
Lesser Honeyguide
Picidae
Cardinal Woodpecker
Lybiidae
White-eared Barbel
Yellow-rumped Tinkerbird
Yellow-fronted Tinkerbird
Red-fronted Tinkerbird
Acacia Pied Barbet
Black-collared Barbet
Crested Barbet
Phoeniculidae
Green Woodhoopoe
Rhinopomastidae
Common Scimitarbill
Coliidae
White-backed Mousebird
Speckled Mousebird
Red-faced Mousebird
Psittacidae
Brown-headed Parrot
Musophagidae
Grey Go-away-bird
Columbidae
Laughing Dove
Cape Turtle Dove
Oriolidae
Black-headed Oriole
Dicruridae
Fork-tailed Drongo
Malaconotidae
Brown-crowned Tchagra
Southern Boubou
Corvidae
Pied Crow
White-necked Raven
Paridae
Grey Penduline Tit
Southern Black Tit
Pycnonotidae
Dark-capped Bulbul
African Red-eyed Bulbul
Cape Bulbul
Sombre Greenbul
Terrestrial Brownbul
Sylviidae
Cape Grassbird
Yellow-bellied Eremomela
Burnt-necked Eremomela
Long-billed Crombec
Arrow-marked Babbler
Scientific Name
SNR Refs.
Indicator minor
In
1
1
3
Dendropicos fuscescens
In
1
1
8
Stactolaema leucotis
Fr/ln
2
1
Pogoniulus bilineatus
Fr/ln
1
-
3
Pogoniulus chrysoconus
Fr/ln
2
-
10
Pogoniulus pusillus
Fr/ln
2
-
1
Tricholaema leucomelas
Fr
2
' 1
1,3,8
Lybius torquatus
Fr/ln
2
1
1,3,8
Trachyphonus vaillantii
In/Fr
1
1
3,8
Phoeniculus purpureus
In
1
1
3
Rhinopomastus cyanomelas
In
1
1
1,3, 8,11
Colius colius
Fr/Fo
2
1
3
Colius striatus
Fr/Fo
4
1
1,2, 3, 8,12
Uroco/ius indicus
Fr/Fo
4
1
1,3,8
Poicephalus cryploxanthus
Fr
4
-
1
Corythaixoides concolor
Fr/Fo
3
1
3,7
Slreptopelia senegalensis
Gr/ln
1
1
1,3,8
Streptopelia capicola
Gr/ln
1
1
1,3
Oriolus larvatus
In/Fr
3
1
1,2, 3, 9,10
Dicrurus adsimilis
In/Ca
3
-
1,2, 3, 9,12
Tchagra australis
In
1
1
8
Laniarius ferrugineus
In/Fr
3
1
1,3
Corns a/bus
Ca/Gr/Fr
1
1
3
Corns albicollis
Ca
3
1
Garland in 1. 3
Anthoscopus caroli
In
3
-
1
Parus niger
In
2
1,3
Pycnonotus tricolor
Fr/ln
4
1
1,3,11
Pycnonotus nigricans
Fr/ln
4
1
3,8
Pycnonotus capensis
Fr
3
-
5
Andropadus importunus
In/Fr
4
-
1,3,12
Phyllastrephus terrestris
In/Fr
4
1
Sphenoeacus afar
In
1
1
3,8
Eremomela icteropygialis
In
1
1
3
Eremomela usticollis
In
2
-
1
Sylvietta rufescens
In
2
1
1,3,8
Turdoides jardineii
In/Fr
2
1,3
Importance of Aloe marlothii for opportunistic avian nectarivores: Symes
Bull ABC Vol 17 No 2 (2010) -185
Species and family
Scientific Name
Feeding Guild
Level of nectarivory
SNR
Refs.
Chestnut-vented Tit-Babbler
Parisoma subcaeruleum
In/Fr
1
1
3,8
Zosteropidae
African Yellow White-eye
Zosterops senegalensis
In/Fr
3
_
1
Cape White-eye
Cisticolidae
Zosterops capensis
In/Fr
4
1
2, 3, 8, 9,10,12
Rattling Cisticola
Cisticola chiniana
In
4
1
1,3,8
Neddicky
Cisticola fulvicapilla
In
4
1
1,3,8
Tawny-flanked Prinia
Prinia subflava
In
3
1
1,3
Black-chested Prinia
Prinia flavicans
In
3
1
3,8
Karoo Prinia
Prinia maculosa
In
1
-
3
Bar-throated Apalis
Apalis thoracica
In
2
1
8
Yellow-breasted Apalis
Apalis flavida
In/Fr
1
-
1,3
Rudd’s Apalis
Apalis ruddi
In
3
-
3
Muscicapidae
1
Cape Rock Thrush
Monticola rupestris
In/Fr
1
1
3, 8,12
Pale Flycatcher
Bradornis pallidus
In/Fr
2
-
1
Southern Black Flycatcher
Melaenornis pammelaina
In/Fr
2
-
1
Fiscal Flycatcher
Sigelus silens
In/Fr
3
1
1,3,8
African Dusky Flycatcher
Muscicapa adusta
In/Fr
2
-
12
Cape Robin-Chat
Cossypha caffra
In/Fr
1
1
8
White-browed Scrub-Robin
Cercotrichas leucophrys
In/Fr
2
-
1
Buff-streaked Chat
Oenanthe bifasciata
In
3
-
3
Mocking Cliff Chat
Sturnidae
Thamnolaea cinnamomeiventris
In/Fr
1
1
3
Red-winged Starling
Onychognathus morio
Fr/ln
3
1
3,4, 7, 9,12
Black-bellied Starling
Lamprotornis corruscus
Fr/ln
3
-
1,3
Cape Glossy Starling
Lamprotornis nitens
In/Fr
3
1
1,3, 7, 8,9
Pied Starling
Spreo bicolor
In/Fr
3
1
3,9
Wattled Starling
Creatophora cinerea
In/Fr
1
1
8
Red-billed Oxpecker*
Nectarinidae
Buphagus erythrorhynchus
In
0
1
8
Olive Sunbird
Cyanomitra olivacea
Hello
5
-
-
Grey Sunbird
Cyanomitra mom
Hello
5
-
-
Amethyst Sunbird
Chalcomitra amethystina
Ne/ln
5
1
2,4,7, 9,12
Scarlet-chested Sunbird
Chalcomitra senegalensis
Ne/ln
5
-
2,7
Bronzy Sunbird
Nectarinia kilimensis
Ne/ln
5
-
2
Malachite Sunbird
Nectarinia famosa
Ne/ln
5
1
2, 7, 8, 9,12
Collared Sunbird
Hedydipna collaris
Ne/ln
5
-
7,12
Southern Double-collared Sunbird
Cinnyris chalybeus
Ne/ln
5
-
2,4, 7,9
Greater Double-collared Sunbird
Cinnyris afer
Ne/ln
5
-
2, 7, 9,12
White-bellied Sunbird
Cinnyris talatala
Ne/ln
5
1
2, 7,8
Dusky Sunbird
Cinnyris fuscus
Ne/ln
5
-
2, 6,9
Marico Sunbird
Cinnyris mariquensis
Ne/ln
5
-
2,6
Promeropidae
Gurney's Sugarbird
Promerops gurneyi
Ne/ln
5
_
2
Cape Sugarbird
Ploceidae
Promerops cater
Ne/ln
5
2
Lesser Masked Weaver
Ploceus intermedius
In/Gr
3
-
5
Spectacled Weaver
Ploceus ocularis
In/Fr/Gr
4
-
1
Cape Weaver
Ploceus capensis
In/Gr
3
1
2, 3, 4, 7, 8, 9
Yellow Weaver
Ploceus subaureus
In/Gr/Fr
4
-
U
Southern Masked Weaver
Ploceus velatus
In/Gr
4
1
1,3,8
186 -Bull ABC Vol 17 No 2 (2010)
Importance of Aloe marlothii for opportunistic avian nectarivores: Synies
Species and family
Village Weaver
Dark-backed Weaver
White-winged Widowbird
Red-collared Widowbird
Estrildidae
Black-faced Waxbill
Common Waxbill
Violet-eared Waxbill
Green-winged Pytilia
Jameson’s Firefinch
Passeridae
House Sparrow
Cape Sparrow
Southern Grey-headed Sparrow
Yellow-throated Petronia
Fringillidae
Black-throated Canary
Yellow-fronted Canary
Yellow Canary
Brimstone Canary
Streaky-headed Seedeater
Cinnamon-breasted Bunting
Cape Bunting
Total number of species
Scientific Name
Ploceus cucullatus
Ploceus bicolor
Euplectes albonotatus
Euplectes ardens
Estrilda erythronotos
Estrilda astrild
Granatina granatina
Pytilia melba
Lagonosticta rhodopareia
Passer domesticus
Passer melanurus
Passer diffusus
Petronia superciliaris
Serious atrogularis
Serious mozambicus
Serious flaviventris
Serious suiphuratus
Serious gularis
Emberiza tahapisi
Emberiza capensis
Feeding Guild
In/Gr
In/Fr
Gr/ln
Gr/ln
Gr/ln
Gr/Fr
Gr
Gr
Gr
Gr/Fr/ln
Gr/ln/Fr
Gr/ln
In/Gr
Gr/ln
Gr/ln/Fo
Gr/ln/Fo
Gr/Fr/Fo
Gr/Fo
Gr/ln
Gr
101
Level of nectarivory
4
2
1
1
1
1
1
1
1
1
1
2
2
1
3
2
3
3
1
1
SNR
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
Refs.
1,2,3
1
3
3,8
3,8
3
8
8
8
3
3
3,8
1,2,3
3,8
1,2,3
3
1,2,3
1,3,4, 8,12
8
8
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Importance of Aloe marlothii for opportunistic avian nectarivoi es: Symes
Bull ABC Vol 17 No 2 (2010) -187
Investigating Lesser Flamingo Phoeniconaias minor
movements and the potential connectivity among
regional populations using satellite-telemetry
Volker Salewski", Brooks Childress h and Martin Wikelski“
Examiner les mouvements du Flamant nain Phoeniconaias minor et la connectivity potentielle parmi
les populations regionales en utilisant des balises argos. Le Flamant nain Phoeniconaias minor est
considere comme « Quasi Menace » parce que ses populations semblent subir une diminution moderement
rapide de leurs effectifs. Le Plan d’Action international pour la Conservation du Flamant nain estime
que la degradation des habitats de reproduction et de nourrissage de Fespece constitue la menace la plus
importante. Une des actions priori taires est de determiner la delimitation et les mouvements des populations
en utilisant des balises argos. En mai 2009, la Vogelwarte Radolfcell de Flnstitut ornithologique Max-
Planck, Allemagne, a entame un projet pour etudier les mouvements des Flamants nains a l’aide de balises
argos, en munissant quatre flamants de balises au Lac Abijatta, Ethiopie. En juin 2009, 15 autres Flamants
nains ont ete equipes de balises au Lac Bogoria, Kenya. Les donnees de haute qualite transmises par les
balises pendant les premieres semaines du projet permettent d’esperer que des decouvertes concernant
Fecologie des mouvements du Flamant nain vont etre faites pendant les annees a venir.
Summary. Lesser Flamingo Phoeniconaias minor is classified as Near Threatened because its populations
appear to be undergoing a moderately rapid reduction. The International Single Species Action Plan for
the Conservation of the Lesser Flamingo identifies the degradation of the species’ breeding and feeding
habitats as the most critical threat. One of the actions given high priority in the action plan is to determine
population delineation and movements using satellite tracking to determine movements between lakes,
interchange and possible gene flow between populations, and site usage. In May 2009, the Vogelwarte
Radolfzell at the Max-Planck Institute for Ornithology, Germany, commenced a project to investigate the
movements of Lesser Flamingos by satellite telemetry, by tagging four Lesser Flamingos with solar-powered
GPS platform transmitter terminals (PTT) at Lake Abijatta, Ethiopia. In June 2009, 15 additional Lesser
Flamingos were equipped with PTTs at Lake Bogoria, Kenya. During the first weeks of the project the
PTTs transmitted high-quality data indicating that in the next few years the project will reveal new insights
into the ecology of Lesser Flamingo movements.
Lesser Flamingo Phoeniconaias minor is the
smallest and most numerous flamingo species
in the world (Childress et al. 2008) and, like all
flamingos, is a habitat specialist. Lesser Flamingos
depend on shallow saline alkaline wetlands in
which they forage mainly on blue-green algae
and benthic diatoms (Ridley et al. 1955, Tuite
1979, 2000). There are four distinct regional
populations in Africa and Asia. Childress et
al. (2008) list 69 key sites, i.e. sites regularly
holding >1% of a regional population, but regular
successful breeding has been confirmed at only six
(Fig. 1). Due to their declining populations, Lesser
Flamingos are categorised as Near Threatened in
the 2009 IUCN Red List of Threatened Species
(BirdLife International 2009). The species is also
listed in columns A and B of the Agreement on
the Conservation of African-Eurasian Migratory
Waterbirds (AEWA) Action Plan, Appendix II
of the Bonn Convention and Appendix II of the
CITES convention (Childress et al. 2008).
There are three distinct regional populations
of Lesser Flamingo in Africa. The world’s largest
concentration, of an estimated 1.5-2. 5 million
individuals, representing >75% of the global
population (Wetlands International 2006), occurs
on soda lakes in the East African Rift Valley
(Brown et al. 1982, Mlingwa & Baker 2006).
However, during the past 50 years regular breeding
of this population has been recorded only at Lake
Natron, Tanzania (Bartholomew & Pennycuick
1973, Brown et al. 1982, Childress et al. 2008).
Historically, Lesser Flamingos were also recorded
breeding at Lake Nakuru, Kenya, with the last
reliable record in 1915 (Meinertzhagen 1958).
Irregular sporadic breeding events have also been
recorded at a few other sites, such as Lake
Turkana, Kenya, in 1957, Lake Magadi, Kenya,
1 88 - Bull ABC Vol 17 No 2 (2010)
Investigating Lesser Flamingo movements: Salewski et al.
Primary range states,
with >1% of regional populations
Occurs regularly,
but supports <1% of regional populations
★
Breeding occurs regularly
☆
Single recent breeding event
Occurs as a vagrant
(has also occured in Denmark and the Netherlands)
Figure 1. Distribution of Lesser Flamingos Phoeniconaias minor (from Childress et al. 2008).
Repartition du Flamant nain Phoeniconaias minor (d’apres Childress et al. 2008).
in 1962 (Brown & Root 1971) and Lake Abijatta,
Ethiopia, in 2005, when successful breeding of the
Lesser Flamingo was recorded for the first time in
the latter country, and a creche of 2,500-3,500
chicks was observed (Bozic & Ewnetu 2008).
A smaller regional population occurs in
southern Africa, with an estimated 55,000-65,000
individuals (Wetlands International 2006). This
population increases during good breeding years
e.g. c.80,000 breeding pairs were counted at
Sua Pan, within the Makgadikgadi, Botswana,
in 2000, and c. 8 5, 000 individuals were present
there in March 2005 (Childress 2005). It has
been speculated that numbers breeding at Sua
Pan may be augmented by birds from countries
not comprehensively included in southern African
population counts, like Angola and Mozambique,
or indeed from further afield (G. McCulloch
pers. comm.). Frequent breeding occurs at Sua
Pan, Botswana, and less frequently at Etosha
Pan in Namibia (Simmons 1996, Borello et al.
1998, McCulloch & Borello 2000, McCulloch
& Irvine 2004). Historically, sporadic breeding
with many fewer individuals involved was also
reported from Zambia (Brown 1957), and since
2007 birds have bred annually on a specially
constructed island in Kamfers Dam, Kimberley,
South Africa, which colony produced c.9,000
chicks in 2007/2008 (Anderson 2008, Childress
et al. 2008). In 2008/2009 almost 15,000 chicks
were counted (M. Anderson pers. comm.). Lesser
Flamingos, thought to be younger individuals,
are well known for attempting to breed at many
sites each year, given suitable local conditions.
However, these attempts usually involve few pairs
(< 500) and are almost invariably unsuccessful.
A small population of 15,000-25,000 Lesser
Flamingos occurs in West Africa (Wetlands
International 2006), with the main concentrations
in the Senegal Delta and its environs (Trolliet &
Fouquet 2001). ‘Large’ concentrations are also
found at coastal sites in northern Mauritania
(Isenmann 2006) and in Guinea, with up to
10,000 individuals (Trolliet & Foquet 2001).
Investigating Lesser Flamingo movements: Salewski et al.
Bull ABC Vol 17 No 2 (2010) -189
Breeding has rarely been reported in West Africa.
A colony of c.800 nests was discovered in 1965 in
southern Mauritania (de Naurois 1965). In the
same area a breeding attempt involving c.200 nests
failed in 1988, apparently due to disturbance by
local hunters (Lamarche 1988). Concentrations of
juveniles and displaying by larger groups of adult
Lesser Flamingos led repeatedly to speculations
that there might be undiscovered breeding sites
in West Africa (Dugan 1984, Hamerlynck &
Messaoud 2000, Diawara et al. 2008).
In South Asia, Lesser Flamingos occur at a
variety of mostly coastal sites between Yemen
and Bangladesh (Mundkur 1997, Childress et
al. 2006), and in the saline wetlands of Gujarat
and Rajasthan states in north-west India. The
Asian population is apparently either subject to
extreme fluctuations or the majority spend their
time at sites not visited by ornithologists during
censuses. Because ol the remoteness of the sites
used by the species in India, a complete census has
been difficult to obtain. The best current estimate
is 390,000 individuals (Wetlands International
2006). Regular breeding is only reported from
several sites in Gujarat in north-west India, with
a maximum of c. 10,000 pairs (Parasharya & Tere
2006). Sporadic breeding has also reported in
the Indian state of Rajasthan (Kumar 1996) and
unsuccessful breeding attempts have been reported
in Yemen (Al-Saghier & Porter 1996).
Intra-population movements of Lesser
Flamingos
Lesser Flamingos generally make regular nomadic
movements between breeding and non-breeding
sites depending on breeding and feeding
conditions. Seasonal migration takes place when
large numbers move from non-breeding feeding
areas to the breeding sites when those sites become
suitable for breeding (e.g. when large pans flood in
southern Africa and India). These movements can
involve distances of several hundred kilometres
(Childress et al. 2007).
In eastern Africa, the numbers of Lesser
Flamingos at certain sites can vary by several tens
of thousands of birds (Vareschi 1978, Tuite 1979,
2000, Mlingwa & Baker 2006). On individual
lakes, their numbers can double or be reduced
by half within the period of a week. Lesser
Flamingos are adapted to respond to changes
in local environmental conditions by moving
Figure 2. Lesser Flamingo / Flamant nain Phoeniconaias
minor , Lake Bogoria, Kenya (Volker Salewski)
elsewhere, and thus depend on a network of
sites (BirdLife International 2000). In 1969,
for example, 960,000 Lesser Flamingos were
counted on just two lakes, Nakuru and Bogoria
in Kenya (Bartholomew & Pennycuick 1973).
Between 1974 and 1976, the number of Lesser
Flamingos recorded on nine lakes in the Rift
Valley of East Africa was much lower (between
430,000 and 540,000: Tuite 2000). The location
of the ‘missing' flamingos was unknown but an
association with relatively high numbers of Lesser
Flamingos in southern Africa was discussed (Tuite
1979, see below). Flowever, the ‘missing’ birds
might also be explained by the fact that the lakes
were not counted concurrently, the censuses
having been conducted over a period of several
months.
Eight Lesser Flamingos were equipped with
satellite transmitters in Kenya in 2002/03. One
of these transmitters failed shortly thereafter, but
the remaining seven birds were followed for up to
four years (BC unpubl.). The flamingos moved
independently with varying flight directions and
distances as well as varying stopover periods at
190 - Bull ABC Vol 17 No 2 (2010)
Investigating Lesser Flamingo movements: Salewski et al.
Figure 3. Lesser Flamingos Phoeniconaias minor flying over Botswana (Graham McCulloch)
Flamants nains Phoeniconaias minor volant au dessus du Botswana (Graham McCulloch)
Figure 4. Lesser Flamingos Phoeniconaias minor bathe in a freshwater spring, Lake Bogoria, Kenya (Volker Salewski)
Flamants nains Phoeniconaias minor se baignant dans une source d’eau douce, Lac Bogoria, Kenya (Volker Salewski)
Investigating Lesser Flamingo movements: Salewski et al.
Bull ABC Vol 17 No 2 (2010) -191
different lakes. There was no clear pattern of the
birds choosing to stay at specific lakes and it was
often the case that one of the tagged birds would
depart from a lake within days of another arriving
at the same site. The entire flyway for all tagged
flamingos consisted of a 940 km north-south
range in the Rift Valley between Lake Logipi,
Kenya, and Lake Bahi, Tanzania (Childress et al.
2007).
Within southern Africa, Borello et al. (1998)
and Childress (2006) discussed indications for
extensive movements of Lesser Flamingos, such as
highly fluctuating numbers in some areas, erratic
breeding events in high concentrations at different
sites, and observations of migrating birds. On
Sua Pan in Botswana, five Lesser Flamingos were
equipped with satellite transmitters of which
two failed shortly after they were fitted. The
remaining three birds stayed for several months at
the original site until the lake dried out. During
the movements that followed their departure
from Sua Pan, south into South Africa, distances
of up to 930 km were covered within a few days
(McCulloch et al. 2003).
In West Africa, scarcely anything is known
about the movements of Lesser Flamingos. The
initiation of breeding in favourable environmental
circumstances (de Naurois 1963, Lamarche
1988), the large fluctuations in the number of
birds in the Senegal Delta from c. 100 to 50,000
individuals (Trolliet & Fouquet 2001), as well as
the surprising discovery of up to c. 10,000 Lesser
Flamingos in Guinea (Altenburg & van der Kamp
1991) indicate wide-ranging movements within
this population. In Asia, the wide distribution
of the species with only few breeding sites is
also indicative of extensive movements. Seasonal
fluctuations are regularly recorded in India
(Parasharya & Tere 2006).
Causes of movements within populations
There are few studies investigating the causes of
movements in Lesser Flamingos. There was a
significant correlation between the density of algae
small enough to be filtered by Lesser Flamingos
and Lesser Flamingo numbers berween December
1972 and 1974 at Lake Nakuru, Kenya (Vareschi
1978). At the same site, Tuite (2000) also found
that over many months between 1974 and 1976,
the number of Lesser Flamingos was positively
associated with the density of the filamentous
Figure 5. Waiting for the Lesser Flamingos Phoeniconaias
minor, basic research camp at Lake Abijatta, Ethiopia
(Volker Salewski)
Attendant les Flamants nains Phoeniconaias minor ; le
camp des chercheurs au Lac Abijatta, Ethiopie (Volker
Salewski)
Figure 6. A Lesser Flamingo Phoeniconaias minor is
equipped with a satellite transmitter (Volker Salewski)
Un Flamant nain Phoeniconaias minor est equipe d’une
balise (Volker Salewski)
Figure 7. A Lesser Flamingo Phoeniconaias minor takes
off after being equipped with a satellite transmitter
(Volker Salewski)
Un Flamant nain Phoeniconaias minor s’envole apres avoir
ete equipe d’une balise (Volker Salewski)
192 -Bull ABC Vol 17 No 2 (2010)
Investigating Lesser Flamingo movements: Salewski et al.
blue-green algae Arthrospira fusiformes (formerly
Spirulina platensis), the main food of the species
in East Africa. In this study, the number of Lesser
Flamingos on Lake Nakuru declined from over
one million individuals in January 1974 to less
than 30,000 in August of the same year, following
a distinct decline of Arthrospira in the first half
of that year. Arthrospira densities show irregular
fluctuations, for unknown reasons. Some peaks
last for several years and the biomass can then
reach values of more than ten times the mean
density. Tune (2000) associated these fluctuations
in their main food type with the distribution of
Lesser Flamingos on the lakes in the East African
Rift Valley. However, according to Vareschi
(1978) there is no positive correlation between the
algal density at different lakes and their flamingo
numbers.
Changes in fresh water availability, lake
water conductivity and disturbance by humans
or predators were considered unlikely to cause
population fluctuations (Vareschi 1978).
The studies using satellite tags on Lesser
Flamingos in East Africa revealed a non-significant
trend showing that individual staging periods were
correlated with local precipitation (Childress et al.
2007). In southern Africa, Borello et al. (1998)
discussed the possibility that movements of Lesser
Flamingos are associated with the movement
of the Intertropical Convergence Zone. Erratic
breeding at Sua Pan appears also to be associated
with high rainfall (Borello et al. 1998) and Lesser
Flamingos arrive at the breeding sites within days
of their flooding (McCulloch & Irvine 2004). For
West Africa, Hamerlynck & Messaoud (2000)
describe the coincidence of high rainfall with the
occurrence of Lesser Flamingos in the Senegal
Delta. For India, Parasharya & Tere (2006) also
mention that numbers of Lesser Flamingos vary
with the inundations of the River Rann in the Rann
of Kachchh. All these studies suggest a connection
between the numbers of Lesser Flamingos and the
availability ol food resources and/or the suitability
of breeding sites, but individual decisions during
non-breeding movements between feeding sites,
whilst probably linked to food availablity are still
little understood.
Movements between populations
There is only one record of a Lesser Flamingo
moving between two regional populations: a
bird that was ringed as a chick in Kenya in 1962
was found dead in the Western Sahara in 1997
(Childress & Hughes 2007). Apparent parallel
fluctuations in the sizes of regional populations
ol Lesser Flamingos have been discussed as an
indication that migrations between regional
populations exist (Borello et al. 1998, Simmons
1996, 2000).
In southern Africa, the unexpected high
numbers of Lesser Flamingos in November 1974
at Sua Pan, coinciding with a decline in numbers in
eastern Africa, suggested migration between these
two regional populations (Vareschi 1978, Borello
et al. 1998). Furthermore, that Lesser Flamingos
show fat deposition like other migrants was seen as
being indicative that the birds could move between
southern and eastern Africa (Simmons 2000). On
the other hand, counts revealing unexpected high
numbers of Lesser Flamingos in southern Africa
could indicate that residents are more numerous
than previously thought, which could explain
high breeding densities without immigration from
eastern Africa (Childress 2006). A coordinated
census was conducted in this region in 2008, but
the results have yet to be reported.
It is unknown whether the Lesser Flamingos
observed regularly in Madagascar, where breeding
has never been recorded, originate from eastern or
southern Africa. Their occurrence in Madagascar,
together with records on some Indian Ocean
islands, has led to speculation about movements
between Africa and India via island hopping
(Borello et al. 1998). For India, Parasharya &
Tere (2006) also suggested possible immigrations
into the subcontinent because of incredible
concentrations during the breeding season.
None of the birds equipped with satellite
tags in Botswana and Kenya moved out of their
regional areas (McCulloch et al. 2003, Childress
et al. 2007). However, a recent molecular study
comparing the populations of eastern and southern
Africa indicated that there is some gene flow
between them, thereby supporting the hypothesis
of at least restricted interchange between the two
populations (Zaccara et al. 2008).
Investigating Lesser Flamingo movements
for science and conservation
One of the key questions in animal ecology is
how environmental heterogeneity and the spatial
distribution of resources influence the distribution
Investigating Lesser Flamingo movements: Salewski et al.
Bull ABC Vol 17 No 2 (2010) -193
Figure 8. Movements of four Lesser Flamingos Phoeniconaias minor
equipped with satellite tags at Lake Abijatta, Ethiopia, in May 2009.
Les mouvements de quatre Flamants nains Phoeniconaias minor equipes
de balises au Lac Abijatta, Ethiopie, en mai 2009.
of individuals in space and time. The selection
of temporary staging sites plays a key role in the
life of mobile organisms, e.g. for reproduction,
predator avoidance or optimal foraging, because in
general resources are not evenly distributed either
spatially or temporally. Highly mobile organisms
like birds can cover relatively large distances
to exploit resources, but these movements are
also related to costs like increased mortality or
decreased physiological condition, with negative
effects, e.g. on predator avoidance or reproduction.
Individual decision-making processes therefore
possess direct fitness consequences and are the
basis lor the evolution of certain traits with
respect to movements. There are, however, few
studies that investigate whether movements of
birds mainly reflect the distribution of resources
or whether there are different individual decision-
making rules that control their movements.
Lesser Flamingos perform erratic long-distance
movements between extremely patchily distributed
foraging sites that also show large, probably
unpredictable, fluctuations of resources over
time. Furthermore, the species uses very few sites
for reproduction within its huge geographical
range and breeding success is strongly related to
unpredictable climatic events. Therefore, Lesser
Flamingos are an ideal species to
study decision-making processes in
connection with animal movements.
Studying the movements of Lesser
Flamingos will reveal important
insights into the biology of the species
and will add to our understanding of
the processes related to the ecology of
animal movements in general.
Understanding the movements of
Lesser Flamingos has a direct applied
aspect concerning the conservation of
the species because the reliance of the
global population on patchy habitat
makes the species very vulnerable
when disturbances at a few key sites
occur. Apart from natural fluctuations
in resources (Tuite 1979, 2000) and
unpredictable conditions at some of the
breeding sites, there are anthropogenic
threats to key sites. Vareschi (1978)
mentioned already that the effluent
from Nakuru’s sewage plant could
contaminate Lake Nakuru, especially
since potentially dangerous industries
were built. The only breeding site of the East African
population, Lake Natron, which is unprotected, is
currently threatened by plans for soda extraction
facilities (Childress et al. 2008). Nocturnally,
migrating Lesser Flamingos are reported to be
killed at powerlines far from their usual feeding
and breeding sites in southern Africa (Borello
et al. 1998, Simmons 2000). In West Africa,
Lamarche (1988) reported that the second known
breeding attempt of this regional population
apparently failed because of disturbance by local
hunters. For India, Parasharya & Tere (2006)
described hunting for meat consumption and egg
collection as important threats, the latter being
the sole cause for the failure of regular breeding
attempts at Purabcheria. Furthermore, collisions
of Lesser Flamingos with utility structures are so
frequent at some sites that local fisherman patrol
the respective areas in the morning to collect the
victims. Childress et al. (2008) suggested that
the most critical threats to Lesser Flamingos are
the degradation of their breeding and feeding
habitats through altered hydrology and water
quality, wetland pollution, extraction of salt and
soda ash, and the disruption of their breeding
colonies by human activities. The aim of the
1 94 - Bull ABC Vol 17 No 2 (2010)
Investigating Lesser Flamingo movements: Salewski et al.
recently published International Single Species
Action Plan lor the Conservation of the Lesser
Flamingo (Childress et al. 2008), is to improve
the conservation status of Lesser Flamingo from
Near Threatened to Least Concern, by seeking to
ensure that all major breeding and feeding sites
are designated as protected areas, maintained in
a good ecological condition and that breeding
colonies are not disturbed, amongst other
measures. The action plan therefore emphasises
that ‘a high priority action for the conservation of
the species is to determine population delineation
and movements by conducting satellite tracking .
. . to determine movements of individuals between
lakes, interchange and possible gene flow between
populations and site usage.’
A new study to investigate movements of
Lesser Flamingos and potential connectivity
between populations
The Vogelwarte Radolfzell at the Max-Planck-
Institute for Ornithology, Germany, was involved
in the first satellite-tracking studies to investigate
movements of Lesser Flamingos in the Rift Valley
of eastern Africa (Childress et al. 2004, 2007).
In a new project, 50 solar-powered GPS satellite
platform transmitter terminals (PTT) were made
available. These PTTs will enable individual
birds to be followed for several years through
the ARGOS system (Toulouse, France). The
data will be stored in www.MoveBank.org and
can be consulted there or in Google Earth. The
intention was to distribute the PTTs among the
West African (10-15 PTTs), East African (15-20
PTTs) and Indian populations (20-25 PTTs)
respectively. Funding for more transmitters is
currently being sought to include the southern
African population. The objectives of the study
are:
• to investigate movements of Lesser Flamingos
within the regional populations;
• to investigate environmental conditions
associated with movements;
• to detect important staging areas;
• to discover possible unknown breeding sites,
e.g. in West Africa;
• to investigate whether there are movements
between the four regional populations;
• to discover routes if movements between
populations occur;
• to assess the importance of different staging
areas;
• to assess threats during the movements and at
important staging areas;
• to initiate conservation strategies at important
staging areas and new breeding sites;
• to raise public awareness through contacts
with various media and local organisations;
• to gain publicity by an internet link to follow
the flamingo movements;
Field work commenced in early May 2009
when three adult male and one adult female Lesser
Flamingos (sexing method based on Childress
et al. 2005) were equipped with GPS satellite
transmitters at Abijatta-Shalla Lakes National
Park in Ethiopia using the methods described
by Childress et al. (2007). Data sent by the
transmitters showed that all four birds stayed in
the park during the period immediately following
capture. In early June, one bird moved in a non-
stop nocturnal flight of 530 km north-northeast
to Lake Abbe, on the Ethiopian / Djibouti border,
followed by a second individual in early July. This
had been the hypothesised direction and flight
path for any connection between the East African
and Indian populations.
In June 2009, 15 additional Lesser Flamingos
were equipped with GPS satellite transmitters at
Lake Bogoria, Kenya. One of the PTTs stopped
working on Lake Nakuru after ten days. The same
direction was followed by seven other birds during
the first four weeks after they were equipped
with the PTTs, which made their way either to
Lake Nakuru, Lake Elmentaita or to both in
succession. Additionally, two flamingos chose
to fly even further, to Lake Natron in northern
Tanzania, the only known regular breeding site
of the East African regional population. One of
these birds returned north again after three days
to Lake Nakuru, whilst the other continued
south to Lake Manyara. The solar-powered GPS
PTTs produced data of much higher quality
than previous transmitters using the Doppler
effect, and it is expected that during the next
three to four years the PTTs will reveal many
more interesting movement patterns leading to a
better understanding of the species’ movements
and ecology, as well as helping to implement new
conservation strategies.
Investigating Lesser Flamingo movements: Salewski et al.
Bull ABC Vol 17 No 2 (2010) -195
Acknowledgements
In Ethiopia, Y. D. Abebe was of invaluable assistance in
organising the trip and the necessary permits, and we
also benefited from the kind support of Y. Tekja and
D. Pawlos from the Ethiopian Wildlife Conservation
Authority. J. Zerihun drove us safely to our field site,
where we were assisted by H. Woshe, T. Hayatoa
and M. Beriso. We are also very grateful to A. Owino
from the Kenya Wildlife Service for organising our
expedition to Lake Bogoria, and to J. Nyunja. The
project benefited from the kind support of Dr S. Kasiki
from the Kenya Wildlife Service, and W. Kimosop. G.
Wanjala and R. Kimosop assisted with the field work.
We thank C. Hall for drawing Fig. 1. M. Anderson
and G. McCulloch kindly shared some unpublished
information.
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Investigating Lesser Flamingo movements: Salewski et al.
Bull ABC Vol 17 No 2 (2010) -197
Brief notes on the birds of Mount Inago,
northern Mozambique
Lincoln D. C. Fishpoot and Julian BaylisJ
Notes sur les oiseaux du Mont Inago, Mozambique du nord. Cet article presente les principaux
resultats du premier inventaire ornithologique du Mont Inago, au nord du Mozambique, qui a eu lieu du
4 au 13 mai 2009. Ce massif, situe a 50 km au nord-est du Monr Namuli, atteint une hauteur de plus de
1.800 m. Au total, 101 especes ont ete observees, dont 86 dans le massif et le reste dans les environs. Les
plus importantes etaient l’Alethe de Cholo Alethe choloensis (Menacee d’extinction), l’Akalat de Gunning
Sheppardia gunningi (Quasi menacee), l’Aigle de Verreaux Aquila verreauxi (apparemment la premiere
donnee pour le Mozambique du nord) et le Bruant du Cap Emberiza capensis vincenti (les premieres
donnees pour le pays depuis la recolte originale en 1936). La superficie de la foret d’Inago et sa repartition
altitudinale n’ont probablement jamais ete tres etendues, et les defrichements recents pour 1’agriculture
sont en train de detruire rapidement ce qui reste. L’avenir des quelques especes forestieres presentes est
done sombre.
Summary. The main findings are given of the first brief ornithological survey of Mount Inago, northern
Mozambique. This massif, 50 km north-east of Mount Namuli, rises to over 1,800 m. One hundred
and one species were recorded of which 86 were found on the massil itself. The most significant were
Cholo Alethe Alethe choloensis (Endangered), East Coast Akalat Sheppardia gunningi (Near Threatened),
Verreaux’s Eagle Aquila verreauxi (apparently the first record for northern Mozambique) and Cape Bunting
Emberiza capensis vincenti (the first records from the country since it was originally collected in 1936). The
area and the altitudinal range ot lorest on Inago historically seem unlikely to have been large, while recent
and continuing clearance for agriculture is rapidly eliminating what remains. The future of the relatively
few forest-dependent species found therefore seems bleak.
Following a brief reconnaissance visit the
previous year, in May 2009 a multi-disciplinary
team of scientists made the First-ever scientific
expedition to investigate the flora and fauna of
Mount Inago, northern Mozambique. Arranged
and led by JB, this visit was one of a series of
explorations of biologically little- and unknown
mountains of northern Mozambique, organised
by the Royal Botanic Gardens, Kew, with funding
from the UK government’s Darwin Initiative.
The main ornithological results of this visit are
presented here, and complement those from two
of the other expeditions organised by this project
which are described in Dowsett-Lemaire (2010).
Mount Inago (Serra Inago) forms part of an
extensive massif of undulating, granitic domes
that rise to over 1,800 m immediately south of the
town of Malema (formally Entre Rios) in Nampula
province, northern Mozambique, and is situated
c. 50 km north-east of the better known Mount
Namuli (Dowsett-Lemaire 2010). Between the
network of inselbergs runs a series of semi-forested
valleys in which strips of riverine forest line the
numerous watercourses in valley bottoms and,
in places, beside streams and gullies on the sides
of the inselbergs. The riverine forest grades into
mid-altitude, semi-deciduous forest in parts of the
wider valley bottoms, where conditions permit
(Figs. 1-3). Both forest types are under severe and
increasing pressure from the local communities
who are clearing them for agriculture, in places
right up to the streamsides. Farmed land is, in
some areas, being abandoned, at least temporarily,
and is covered with ‘farmbush’ tangles. There are
also extensive areas of tall grassland which, in some
places, also occur under areas of open woodland.
The inselbergs themselves are sparsely vegetated
with a distinctive flora of low grassland, herbs and
shrubs, several of them succulent or showing other
adaptations to the harsh conditions of the open
rock face. At lower altitudes there are patches of
denser woodland and thicket, particularly along
watercourses, while the region surrounding the
massif supports savanna woodland, including
miombo, now extensively degraded or completely
cleared for agriculture, such that no intact areas of
any size were seen.
198 -Bull ABC Vol 17 No 2 (2010)
Birds of Mount Inago, northern Mozambique: Fishpool & Bayliss
Figures 1-3. Landscape at Mount Inago, northern
Mozambique, May 2009 (Fig. 1 by Julian Bayliss, Figs. 2
and 3 by Lincoln Fishpool)
Paysage du Mont Inago, Mozambique du nord, mai
2009 (Fig. 1 de Julian Bayliss, Figs. 2 et 3 de Lincoln
Fishpool)
The Mount Inago area was visited on 4-13
May 2009. The main campsite was located
at 15°02’42”S 37°23’46”E, at 1,048 m in a
valley bottom between two inselbergs, near the
confluence of two noisy, fast-flowing streams
beside which there was a very narrow strip of
remnant riverine forest. 1 he campsite itself was
on abandoned cultivation, with areas of rank
secondary savanna grassland nearby; five nights
were spent here. In addition, one night was spent
at the 'forest campsite’ (15°04’48”S 37°23’24”E,
1,478 m), at the foot of another inselberg within
a relatively large forest patch, parts of which were
being cleared for maize cultivation, while other
parts had been cleared in the recent past.
In total, 101 species were recorded, of which
86 were found in the massif complex itself, with
the remainder seen in nearby Malema town or
in the wider area. Since by far the majority of
these were common, widespread species whose
presence was unremarkable, the full list is not
presented here but appears in Bayliss et al. (2010)
and is available upon request from the authors.
However, some species worthy of comment were
found and since these are, apparently, the first
ornithological records from Mount Inago, they are
discussed below. Further background information
on Inago, details of the expedition itself and of its
botanical and other zoological discoveries are also
provided by Bayliss et al. (2010). Notable among
the latter are a new species of pygmy chameleon
(. Rhampholeon sp.), butterfly ( Cymothoe sp.),
freshwater crab ( Potamonautes sp.), and a possible
new species of cycad ( Encephalartos sp.).
Notes on selected species
Verreaux’s Eagle Aquila verreauxi
A pair was soaring above an inselberg on 6 May.
Not known from adjacent Namuli (Ryan et al.
1999, Dowsett-Lemaire 2008) and there seem to
be no previous records from northern Mozambique
(Frade 1933). It is a rare bird anywhere in the
country; Parker (1999, 2005) estimated that in
the south and centre of Mozambique there were
'possibly fewer than five breeding pairs and
'6 to 20 breeding pairs’ respectively. No firm
evidence was found on Inago of the eagle’s main
prey species, Rock Hyrax Procavia capensis. None
was heard calling which, if they were present, is
surprising, even allowing for the volume of noise
from the stream by the campsite. Many parts of
the domes were, however, littered with abundant
droppings of a size and shape that suggested
hyrax. Alternatively, these could have all been
attributable to Smith’s Red Rock Hare Pronolagus
rupestris, which was seen on several occasions.
Birds of Mount Inago, northern Mozambique: Fishpool & Bayliss
Bull ABC Vol 17 No 2 (2010) -199
Silvery-cheeked Hornbill Bycanistes brevis /
Trumpeter Hornbill B. bucinator
A pair of Silvery-cheeked Hornbills was seen
visiting forest remnants on three dates, whilst a
pair of Trumpeter Hornbills was recorded over
the main campsite twice. Records of these two
hornbills are of interest because they are usually,
but not always, allopatric in Malawi (Dowsett-
Lemaire & Dowsett 2006). Although not seen
together on Inago, there was no obvious altitudinal
or habitat separation between these observations;
the Trumpeters were, however, only seen 'passing
through’ or along what was in effect a narrow
corridor between adjacent inselbergs.
Cholo Alethe Alethe choloensis (Endangered)
One was trapped in a mist-net at the forest
campsite. Its occurrence is notable as being one of
the few Afromontane species found.
East Coast Akalat Sheppardia gunningi (Near
Threatened)
One was seen in the forest remnant beside the
stream at the main campsite; two were mist-netted
at the forest campsite. Not known from adjacent
Namuli (Ryan et al. 1999, Dowsett-Lemaire
2008), presumably because no forest now remains
there at suitable altitudes.
Magpie Mannikin Spermestes fringilloides
Three individuals of this uncommon species were
seen together on one occasion near the main
campsite. It is probably relevant that stands of the
bamboo Oxytenanthera were present in the general
environs.
Cape Bunting Emberiza capensis
A pair was seen on an inselberg close to the main
campsite on three dates. With the breast dark
grey merging to brownish on the belly and just
a small rufous patch on the wing-coverts, these
were clearly of the race vincenti. Although quite
widespread in suitable habitat in neighbouring
Malawi (Dowsett-Lemaire & Dowsett 2006),
these appear to be the first records of vincenti in
Mozambique since the type series was collected at
Zobue on the Malawi border, west of Blantyre,
with others from Mirrote (13°50’S 39°34’E),
c.265 km north-east of Inago (Vincent 1936).
This is contra Fry (2004) who — treating vincenti
as a species separate from capensis — states that
there are records of it from Mangochi Mts. {sic)
on both sides of the Malawi/ Mozambique border,
referencing Hall & Moreau (1970) as the source.
Since, however, nothing in Hall & Moreau
(1970) explicitly supports records from this part
of Mozambique and as, moreover, Mangochi
Mountain (singular) lies entirely within Malawi
(F. Dowsett-Lemaire in litt. 2010), this appears
to be an error.
While therefore not yet reported from adjacent
Namuli or nearby Mabu (Ryan et al. 1999,
Dowsett-Lemaire 2008, 2010), ir is probably
more widespread in the region, given the amount
of suitable habitat.
Discussion
The discovery of East Coast Akalat on Mabu
(Spottiswoode et al. 2008, Dowsett-Lemaire 2010)
and now at Inago suggests that it may be relatively
widespread in this part of Mozambique — or,
rather, may have been. Given the rate of forest
destruction witnessed, the future of this and other
forest-dependent species, including Cholo Alethe,
on Inago, is bleak. If true of other areas of remnant
forest at comparable altitudes associated with a
number of as yet unexplored inselbergs in the
area, then Dowsett-Lemaire’s (2010) assessment
of the importance of the population on Mabu is
correct.
The few forest-dependent species found
included White-eared Barbet Stactolaema leucotis ,
Little Greenbul Andropadus virens, Grey-olive
Greenbul Phyllastrephus cerviniventris , Cabanis’s
Greenbul P. cabanisi, Yellow-streaked Greenbul P.
flavostriatus , Blue-mantled Flycatcher Trochocercus
cyanomelas and Square-tailed Drongo Dicrurus
ludwigii. Black-headed Apalis Apalis melanocephala ,
another forest species, also occurred, sharing its
habitat with Yellow-breasted Apalis A. flavida, the
presence of which suggests (but does not eliminate
the possibility) that Namuli Apalis A. ( thoracica )
lynesi does not occur on Inago, although Namuli
is just c.50 km distant.
The much lower altitudes of the forest
on Inago probably explain this absence. It is
perhaps telling that, apart from Cholo Alethe,
the only other Afromontane species recorded
were Cabanis’s Greenbul, Swee Waxbill Estrilda
melanotis and African Citril Serinus citrinelloides.
Indeed, although this visit was so brief that it
is extremely improbable that a full inventory
Birds of Mount Inago, northern Mozambique: Fishpool & Bayliss
200 -Bull ABC Vol 17 No 2 (2010)
of die species of Inago has been made, the size,
topography and altitudinal range of the massif
means that the extent of forest here, particularly
at higher altitudes, can never have been large,
and it is therefore likely that the forest-dependent
avifauna was correspondingly limited.
Such was the extent of forest destruction seen
on Inago that, in truth, we were rather relieved
not to find additional forest-dependent species.
While Bayliss et al. (2010) make a number of
recommendations for promoting the conservation
of what forest remains, the urgency of the case,
coupled with other demands for conservation
effort in the region, means that the chances of
them being realised, regrettably, appear remote.
Acknowledgements
The expedition formed part of the British government-
funded Darwin Initiative project ‘Monitoring and
Managing Biodiversity Loss on South-East Africa’s
Montane Ecosystems’ (Award 15/036). This
collaborative project, led by the Royal Botanic Gardens,
Kew, also included BirdLife International, the Instituto
de Investigagao Agraria de Mozambique, the Mulanje
Mountain Conservation Trust, Malawi, and the Forest
Research Institute of Malawi. The African Butterfly
Research Institute, Nairobi, also participated in this
expedition, and provided some of the funding. Thanks
go to Hassan Patel for assistance in the field, to Mark
Balman and Graeme Buchanan for the provision and
interpretation of satellite imagery, and to Franqoise
Dowsett-Lemaire for advice on the preparation of this
note and help with some references.
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birdlife.org
bMulanje Mountain Conservation Trust (MMCT), PO
Box 139, Mulanje, Malawi and Conservation Science
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Birds of Mount Inago, northern Mozambique: Fishpool & Bayliss
Bull ABC Vol 17 No 2 (2010) - 201
The Slender-billed Curlew Numenius tenuirostris in Africa
Graeme Buchanan", Nicola Crockford' and Adam Gretton1’
Le Courlis a bee grele Numenius tenuirostris en Afrique. La derniere observation du Courlis a bee grele
Numenius tenuirostris, une espece consideree comme « Gravement menace d’extinction », date d’avril 2001
en Hongrie. L’article passe en revue les mentions du courlis en Afrique du Nord et ailleurs en Afrique
(Seychelles, Djibouti, Soudan, Chad, Gambie), en se basant sur les donnees rassemblees par le Groupe de
travail du Courlis a bee grele (http://www.slenderbilledcurlew.net), afin d’identifier les zones potentielles
ou chercher l’espece et la meilleure periode pour le faire.
The Slender-billed Curlew Numenius
tenuirostris (Fig. 1) is a Critically Endangered
species and the only ‘lost' species in the Western
Palaearctic, with no verified records for almost a
decade (the Hungarian Rarities Committee has
accepted a record from April 2001 in Kiskunsag
National Park: Olah & Pigniczki in press). The
population has declined dramatically over the
past century, with loss of habitat and hunting
pressure considered the key likely causes (BirdLife
International 2009a). The only verified breeding
site, recorded during the first quarter of the 20th
century, is north ol Omsk, in southern Siberia
(Gretton et al. 2002). There are passage, and
other non-breeding season records of the species
from across Europe (Delany et al. 2009). Whilst
there are also a few non-breeding records from the
Middle East, North Africa is the main known non-
breeding area for Slender-billed Curlew. Indeed,
the species was first described from a specimen
shot in Egypt in 1817.
The best known site for the Slender-billed
Curlew is Merja Zerga, in Morocco, where birds
were regularly recorded between the 1950s and
February 1995 (Fig. 2), since when there have
been no confirmed sightings in North Africa.
However, the species might still be present in the
region, given that two much more conspicuous
globally threatened bird populations have recently
been discovered within the range of the Slender-
billed Curlew, namely those of Sociable Lapwing
Vanellus gregarius (BirdLife International 2009b)
and, in Syria, the only natural breeding colony
of Northern Bald Ibis Geronticus eremita outside
Figure 1. Slender-billed Curlew Numenius tenuirostris (left) with Eurasian Curlew N. arquata orientals in Yemen,
October 1984 (Richard Porter)
Courlis a bee grele Numenius tenuirostris (a gauche) avec Courlis cendre N. arquata orientals au Yemen, octobre 1984
(Richard Porter)
202 - Bull ABC Vol 17 No 2 (2010)
The Slender-billed Curlew in Africa: Buchanan et al.
Figure 2. Slender-billed Curlews Numenius tenuirostris in
Morocco, January 1994 (Brayton Hole)
Courlis a bee grele Numenius tenuirostris au Maroc,
janvier 1994 (Brayton Holt)
Morocco (BirdLife International 2009c). Here
we review records of Slender-billed Curlew in
North Africa, together with a few records from
outlying countries (Seychelles, Djibouti, Sudan,
Chad, Gambia), based on records collated by the
Slender-billed Curlew Working Group (http://
www.slenderbilledcurlew.net). We do so in order
to identify potential areas for searches, and the
optimum time to visit these locations.
Geographic distribution of Slender-billed
Curlew records
The distribution of records from North Africa
by year (each location in each year counted
only once, even if birds were recorded multiple
times) indicates that the number of records of
Slender-billed Curlew slowly increased during
the 20th century (Fig. 3), especially after 1970.
This increase was probably the result of a greater
awareness of the species, plus the greater number
of experienced European birdwatchers travelling
to North Africa. However, the number of records
then crashes post-1995.
Despite the popularity of one site (Merja Zerga
in Morocco) at this time, it is notable that a large
number of records came from elsewhere during
the period between 1970 and 2000. This suggests
that, while it held the largest known population
(up to 12 birds in some years), it was not the only
area where birds were recorded in North Africa at
this time. The majority of records (each location
in each year counted only once, even if birds were
recorded multiple times) of Slender-billed Curlew
in North Africa come from Morocco (Figs. 4-5).
The majority of sightings are from Merja Zerga,
but even this well-watched site only accounted for
Figure 3. Distribution of Slender-billed Curlew
Numenius tenuirostris records in North Africa by year
since 1850. Record defined as a sighting in a location in
a year. Black = unverified records; grey = verified records;
pale grey = records from Merja Zerga, Morocco.
Repartition des donnees du Courlis a bee grele Numenius
tenuirostris en Afrique du Nord par annee depuis 1850.
Donnee definie comme une observation en une localite
en une annee. Noir = donnees non verifiees ; gris =
donnees verifiees ; gris hachure = donnees de Merja
Zerga, Maroc.
Figure 4. Distribution of Slender-billed Curlew
Numenius tenuirostris records in African countries since
1850. Record defined as sighting in a location in a year.
Black = unverified records; grey = verified records; pale
grey = records from Merja Zerga, Morocco.
Repartition des donnees du Courlis a bee grele Numenius
tenuirostris en Afrique par annee depuis 1850. Donnee
definie comme une observation en une localite en une
annee. Noir = donnees non verifiees ; gris = donnees
verifiees ; gris hachure = donnees de Merja Zerga, Maroc.
some 21% of the Moroccan records. Tunisia had
the next largest number of records after Morocco,
with the majority of these coming from the area
around Kairouan, Metbassta.
The Slender-billed Curlew in Africa: Buchanan et al.
Bull ABC Vol 17 No 2 (2010) - 203
Figure 5. Distribution of accepted Slender-billed Curlew Numenius tenuirostris records in North Africa between 1900
and 2000.
Repartition des donnees acceptees du Courlis a bee grele Numenius tenuirostris en Afrique du Nord entre 1900 et 2000.
□ Pfe 1900 ■ 1 900 - 1920 0 1921 - 1940 o 1941 - 1960 o 1961 - 1980 0 1981 - present
Figure 6. Distribution of confirmed Slender-billed
Curlew Numenius tenuirostris records in North Africa by
month since 1850, subdivided by 20-year time periods.
Repartition des donnees acceptees du Courlis a bee grele
Numenius tenuirostris en Afrique du Nord par mois
depuis 1850, subdivisees par periodes de 20 ans.
The distribution of records will reflect the
distribution of observers, with the best-known sites
being better watched. The paucity of records from
Libya and Algeria might therefore be misleading,
and these countries could potentially have held
non-breeding populations too. In addition to
possible records from the Red Sea coasts of Sudan
and Djibouti, outlying reports come from inland
Chad, with a couple of records from Seychelles.
There are further records from Lanzarote, in the
Canaries, and two undocumented reports from
The Gambia.
Behaviour in North Africa
The majority of records of Slender-billed Curlew
in North Africa appear to be close to the sea
(Fig. 5). Indeed, 91.5% of the 142 sites with
Slender-billed Curlew records are within 1 km of
the coast. Unfortunately, it is difficult to assess
the habitats at these sites since land cover might
have changed during the intervening period, but
analysis based on land cover type within 1 km of
sightings, using GlobCover 2005 (ESA 2009),
indicates that the major habitat was open water,
covering some 29.5% of the area. Mosaics of
grasslands and arable covered 26%, whilst sparse
vegetation or bare areas covered 8% each.
The predominance ol open water could partly
reflect the tendency of birdwatchers to focus on
such areas, whereas observations of the Merja
Zerga birds suggest that they would often feed on
dry sandy farmland 1-2 km from the wetland, as
well as sometimes using grazed marshy areas closer
to the lagoon. There was a striking difference in
204 - Bull ABC Vol 17 No 2 (2010)
The Slender-billed Curlew in A frica: Buchanan et al.
habitat use between years: in the non-breeding
season of 1987—88, most toraging was in the
brackish grazed marsh close to the lagoon, but in
subsequent years the birds usually fed on the higher
sandy land further from the lagoon. This area was
a mixture of cultivated arable strips and fallow
areas, and was used by feeding Eurasian Curlew
Numenius arquata, with which the Slender-billed
Curlews associated (together with Black-tailed
Godwits Limosa limosa). The mudflats of the
lagoon itself were used by roosting Slender-billed
Curlews, usually together with Eurasian Curlew. At
Merja Zerga the Slender-billed Curlews generally
had a regular pattern, feeding for 2-4 hours after
dawn, then roosting in the lagoon, before feeding
again from mid-afternoon until near dusk, when
they again roosted in the lagoon (Gretton 1991).
In this situation, it would be extremely unlikely
that a survey between approximately 10.00 hrs
and 15.00 hrs would have detected the birds, and
we recommend this be taken into account at sites
where a similar pattern could apply.
Temporal distribution of records
The majority of records in North Africa over the
years have consistently come from January (Fig. 6),
with just under 50% of records in December and
February. There are few records between March
and September, which is when birds are either on
passage through Europe or at the breeding sites.
Birds appear to start returning to some sites at
least as early as September, with similar numbers
in October. Oddly, all records from November
come from post- 1981, even though records in
surrounding months come from all time periods.
Slender-billed Curlew conservation
Finding the areas used by Slender-billed Curlews
through the year is a priority lor their conservation.
Conservation efforts are being led by the Slender-
billed Curlew Working Group, founded under the
framework of an international Memorandum ol
Understanding for the species under the United
Nations Convention on Migratory Species. To
help find areas where the bird still occurs, a
top priority of the Group is to encourage a
search of the potential non-breeding range of the
species, which extends across North Africa to the
Middle East, and beyond (if subsequent research
narrows the search for the breeding grounds,
then the search could be extended there too).
If appropriate, any birds that are found will be
caught and satellite-tagged. The satellite tags will
help locate the key sites for the bird throughout its
annual cycle and thus enable urgent conservation
action to be taken. The main focus of the search
is on the known non-breeding and potential
moult sites because it is more likely that birds
will be present long enough to enable catching
and tagging. The priority is to search sites where
the species has previously been recorded, but
also to check those with similar characteristics to
historical sites. A protocol on search methodology
has been produced to provide guidance to those
joining the search (www.slenderbilledcurlew.net).
We encourage observers, whether local or through
expeditions, to check potential areas. Areas of
potentially suitable habitat could be identified
using Google Earth prior to undertaking field
work. Furthermore, to help narrow the search,
observers are requested to submit any past records,
including any ‘possible’ sightings.
Conclusion
Based on a broad-scale examination of the database
of historical records, and a detailed review of key
historical sites for Slender-billed Curlew, we have
identified those site characteristics that could be
useful in targeting field surveys in the search for
the species’ non-breeding areas in North Africa.
Because Slender-billed Curlew poses identification
challenges and because its habitat might include
inland feeding areas that do not tend to be
frequented by birders, and inaccessible inter-tidal
roost areas out of range of most observers, there
is a real chance that it has been overlooked. We
suggest that surveys should be targeted on areas of
the North African coast, from Morocco to Egypt,
within a couple of kilometres of the coastline.
Large-scale habitat analysis does not particularly
limit areas to be searched, but historical records
suggest attention should focus on lagoons and
estuaries, and areas of adjacent feeding habitat
(not just wetlands, bearing in mind the preference
for dry sandy feeding areas at Merja Zerga). It
is of paramount importance that any records of
birds that could still be present in the field are
immediately reported to the Working Group to
facilitate rapid reaction to help verify the record
and undertake conservation action, including
fitting a satellite tag.
The Slender-billed Curlew in Africa: Buchanan et al.
Bull ABC Vol 17 No 2 (2010) - 205
Please send records/digital images/sound
recordings etc immediately to the Slender-
billed Curlew Working Group Coordinator:
timcleeves@yahoo. co.uk, mobile +44
7920050670, 11 Plessey Crescent, Whitley
Bay, Tyne & Wear NE25 8QJ, UK, and
the Slender-billed Working Group Chair
Nicola.crockford@rspb.org.uk, tel. +44 1767
680551.
Acknowledgements
Thanks to all ol the observers who have submitted
details to the SBCWG database, and all those who have
helped manage it, including R. Ahmed, J. Hatt and
I. Fisher. We thank Tim Dodman for comments on
an earlier version ol this text, and Richard Porter and
Brayton Holt for their images.
References
BirdLife International. 2009a. Species factsheet:
Numenius tenuirostris. www.birdlife.org (accessed 2
November 2009).
BirdLife International. 2009b. Species factsheet:
Vanellus gregarius. www.birdlife.org (accessed 2
November 2009).
BirdLife International. 2009c. Species factsheet:
Geronticus eremita. www.birdlife.org (accessed 2
November 2009).
Delany, S., Dodman, T., Stroud, D. & Scott, D. 2009.
An Atlas of Wader Populations in Africa and Western
Eurasia. Wageningen: Wetlands International.
ESA. 2009. GlobCover Project, led by MEDIAS-
France. http://ionial .esrin.esa.int/index.asp.
Gretton, A., Yurlov, A. K. & Boere, G. C. 2002. Where
does the Slender-billed Curlew nest and what
future does it have? Br. Birds 95: 334-344.
Gretton, A. 1991. The Ecology and Conservation of
the Slender-billed Curlew. Cambridge, UK:
International Council for Bird Preservation.
Olah, J. & Pigniczki, C. in press. The first XXIst
century record of Slender-billed Curlew ( Numenius
tenuirostris ) in Hungary. Aquila 116.
" Royal Society for the Protection of Birds, The Lodge,
Sandy, Bedfordshire SGI 9 2DL, UK.
bCosford Hall, Ivy Tree Lane, Hadleigh, Suffolk LP7
6DR.
Received 4 November 2009.
Birding & Beyond Safaris
Tanzania Birding
A specialised bird watching safari operator providing
East African safaris to Tanzania, Kenya and Uganda.
Operating big game and professional bird photographic
safaris for individuals, small groups and families.
P.O. Box 11500 Arusha, Tanzania
Tel: +255 754 286058
tours@tanzaniabirding.com
www.tanzaniabirding.com
206 -Bull ABC Vol 17 No 2 (2010)
The Slender-billed Curlew in Afiica: Buchanan et al.
Hybrid Eurasian Coot Fulica atra x Common Moorhen
Gallinula chloropus on Tenerife, Canary Islands
Beneharo Rodriguez!1, Juan Curbelob and Nazaret Carrasco1'
Un hybride de Foulque macroule Fulica atra x Gallinule poule-d’eau Gallinula chloropus a Tenerife,
lies Canaries. Le premier hybride de Foulque macroule Fulica atra x Gallinule poule-d eau Gallinula
chloropus de Tenerife, lies Canaries, a ete photographic en octobre 2009— janvier 2010. L’hybride etait un
peu plus grand qu une foulque et ne possedait pas de ligne blanche le long des flancs, mais le plumage
et le bee avaient la couleur et le pattern d une poule dean. Ceci correspond avec la coloration et les
caracteristiques morphologiques des hybrides observes sur differents sites en Europe.
Hybrids of Eurasian Coot Fulica atra and
Common Moorhen Gallinula chloropus have
been reported from several sites in Europe (see
van Balen et al. 2001 and references therein). All
described individuals were quite similar, usually
having the size of a coot and lacking any white on
the flanks, but having the bill colour and pattern,
white undertail and green legs of a moorhen (e.g.
Flower 1983, van Balen et al. 2001, McCarthy
2006). Some hybrids can resemble American Coot
F. americana (Moore & Piotrowski 1983). These
features should permit observers to distinguish
hybrids from any other rail species (Taylor
1996).
On 23 October 2009, we observed a hybrid
Eurasian Coot x Common Moorhen at a large
water reservoir (125 x 60 m) with vertical concrete
sides at Los Silos, north-west Tenerife, in the
Canary Islands. It was in the company of an
adult Eurasian Coot and an adult and a juvenile
Common Moorhen. The hybrid was slightly
larger than a coot and had the colour pattern of a
moorhen but lacked the white line on the flanks
(Figs. 1-6). The bill was similar in shape to a
coot’s (with a black wedge in front of the eye),
but had the typical yellow-and-red pattern of a
moorhen, although the ‘red’ was more orange.
The legs, observed briefly when the bird was
preening or flying, were greenish like those of a
moorhen but the toes had enlarged lateral lobes
as in a coot (Fig. 4). The wing-coverts lacked any
white, but the secondaries were browner than the
back (Figs. 1-3).
In total we spent more than four hours
observing and photographing the hybrid during
several visits in October 2009-January 2010.
Several moorhens and coots were always present,
and usually all of the birds remained close
together.
Figures 1-2. Hybrid Eurasian Coot Fulica atra x Common Moorhen Gallinula chloropus, Los Silos, Tenerife, Canary
Islands, January 2010 (Beneharo Rodriguez)
Hybride de Foulque macroule Fulica atra x Gallinule poule-d’eau Gallinula chloropus, Los Silos, Tenerife, lies Canaries,
janvier 2010 (Beneharo Rodriguez)
Hybrid Eurasian Coot x Common Moorhen in Tenerife: Rodriguez et al.
Bull ABC Vol 17 No 2 (2010) - 207
Figures 3-4. Hybrid Eurasian Coot Fulica atra x Common Moorhen Gallinula chloropus with adult Common
Moorhen, Los Silos, Tenerife, Canary Islands, January 2010 (left) and October 2009; note the hybrid’s large size, the
lack of white on the flanks, and the green legs and lobed toes (Beneharo Rodriguez)
Hybride de Foulque macroule Fulica atra x Gallinule poule-d’eau Gallinula chloropus a cote d'une Gallinule poule-
d’eau adulte, Los Silos, Tenerife, lies Canaries, janvier 2010 (a gauche) et octobre 2009 (Beneharo Rodriguez). Noter la
grande taille de l’hybride, l’absence de ligne blanche le long des flancs, et les pattes vertes aux orteils pourvus de lobes.
Figure 5. Hybrid Eurasian Coot Fulica atra x Common
Moorhen Gallinula chloropus with adult Eurasian Coot
and adult Common Moorhen, Los Silos, Tenerife,
Canary Islands, January 2010 (Beneharo Rodriguez)
Hybride de Foulque macroule Fulica atra x Gallinule
poule-d’eau Gallinula chloropus a cote d une Foulque
macroule et une Gallinule poule-d’eau adultes, Los
Silos, Tenerife, lies Canaries, janvier 2010 (Beneharo
Rodriguez)
Figure 6 (above right). Hybrid Eurasian Coot Fulica
atra x Common Moorhen Gallinula chloropus with adult
Eurasian Coot, Los Silos, Tenerife, Canary Islands,
October 2009 (Beneharo Rodriguez)
Hybride de Foulque macroule Fulica atra x Gallinule
poule-d’eau Gallinula chloropus a cote d une Foulque
macroule adulte, Los Silos, Tenerife, lies Canaries,
octobre 2009 (Beneharo Rodriguez)
Figure 7. Hybrid Eurasian Coot Fulica atra x Common
Moorhen Gallinula chloropus, Tejina ponds, Tenerife,
Canary Islands, February 2010 (Beneharo Rodriguez)
Hybride de Foulque macroule Fulica atra x Gallinule
poule-d’eau Gallinula chloropus, etangs de Tejina,
Tenerife, lies Canaries, fevrier 2010 (Beneharo
Rodriguez)
208 - Bull ABC Vol 17 No 2 (2010)
Hybrid Eurasian Coot x Common Moorhen in Tenerife: Rodriguez et al.
We have noted at least one breeding attempt
by a pair of Common Moorhens on this reservoir,
in August 2008, but none by Eurasian Coot,
although individuals of the latter species are
usually present, especially in winter (pers. obs.). At
other sites on Tenerife (e.g. Erjos, Tejina ponds)
and elsewhere in the Canaries both species breed
in close proximity, despite behaving aggressively
towards each other (Fernandez del Castillo 2007,
Barone & Lorenzo 2007). On 21 February 2010,
we found a hybrid Eurasian Coot x Common
Moorhen apparently identical to the Los Silos
hybrid at Tejina ponds, north-east Tenerife, >47
km from the first site (Fig. 7). As we did not
observe the bird there during subsequent visits, we
suspect that it was the Los Silos individual.
The hybrid documented here is apparently
the first for the Canaries (Martin & Lorenzo
2001, Clarke 2006), which is the western limit of
Palearctic breeding populations of both Eurasian
Coot and Common Moorhen. Because hybrids
are very conspicuous (Randier 2004), the previous
lack of observations in the islands could reflect
the limited number of observers, the two species’
small breeding populations (Tenerife has c.50
breeding pairs of Eurasian Coot and 50-100 pairs
of Common Moorhen), or their slight differences
in breeding habitat (more open wetlands for
Eurasian Coot, small ponds with vegetated shores
for Common Moorhen: Sanchez-Zapata et al.
2005, Barone & Lorenzo 2007, Fernandez del
Castillo 2007), limiting the opportunity for mixed
pairings (Randier 2006).
Acknowledgements
We are grateful to Airam Rodriguez for helping us to
photograph the birds, and to Ruben Barone, Bas van
Balen, Harvey van Diek and Ron Demey for suggesting
improvements to an earlier draft of this note.
References
van Balen, J. H., Perdeck, A. C. & van Diek, H. 2001 .
Hybridisatie tussen Waterhoen en Meerkoet. Dutch
Birdingiy. 196-203.
Barone, R. & Lorenzo, J. A. 2007. Focha comun
Fulica atra. In Lorenzo, J. A. (ed.) Atlas de las Aves
Nidificantes en el Archipielago Canario. Madrid:
Direccion General de Conservacion de la Naturaleza
& Sociedad Espanola de Ornitologia.
Clarke, T. 2006. Field Guide to the Birds of the Atlantic
Islands. London, UK: Christopher Helm.
Fernandez del Castillo, M. 2007. Gallineta comun
Gallinula chloropus. In Lorenzo, J. A. (ed.) Atlas
de las Aves Nidificantes en el Archipielago Canario.
Madrid: Direccion General de Conservacion de la
Naturaleza & Sociedad Espanola de Ornitologia.
Flower, G. 1983. Hybrid Coot x Moorhen in North
Yorkshire. Br. Birds 76: 409-410.
Martin, A. & Lorenzo, J. A. 2001. Aves del Archipielago
Canario. La Laguna: Ed. Lemus.
McCarthy, E. M. 2006. Handbook of Avian Hybrids of
the World. New York: Oxford University Press.
Moore, D. R. & Piotrowski, S. J. 1983. Hybrid Coot
x Moorhen resembling American Coot in Suffolk.
Br. Birds 76: 407-409.
Randier, C. 2004. Frequency of bird hybrids: does
detectability make all the difference? J. Ornithol.
145: 123-128.
Randier, C. 2006. Behavioural and ecological correlates
of natural hybridisation in birds. Ibis 148: 459 —
467.
Taylor, P. B. 1996. Family Rallidae (rails, gallinules
and coots). In del Hoyo, J., Elliott, A. & Sargatal,
J. (eds.) Handbook of the Birds of the World. Vol. 3.
Barcelona: Lynx Edicions.
" La Malecita s/n, 38480 Buenavista del Norte, Tenerife,
Canary Islands, Spain. E-mail: benerguez@terra. es
bAjoque, N° 8, 38480 Buenavista del Norte, Tenerife,
Canary Islands, Spain.
Received 3 December 2009; revision accepted 6 June
2010.
Hybrid Eurasian Coot x Common Moorhen in Tenerife: Rodriguez et al.
Bull ABC Vol 17 No 2 (2010) - 209
Rock Firefinch Lagonosticta sanguinodorsalis in the Mandara
Mountains, north-east Nigeria: a new subspecies?
Jacinta I. A balakcf, Ulf Ottosson", Talatu Tend?' and Keith Larsonb
L’Amarante des rochers Lagonosticta sanguinodorsalis dans les Monts Mandara, Nigeria du sud-est :
une nouvelle sous-espece ? Nous fournissons une description d un male et d une femelle, ainsi que des
photos d’un male, d un amarante capture dans les Monts Mandara, au nord-est du Nigeria. Le plumage
et le cri de cet amarante sont identiques a ceux de l’Amarante des rochers Lagonosticta sanguinodorsalis ,
une espece precedemment rapportee de la zone, excepte que le male n’a pas la couronne grise typique de
l’espece. Des travaux supplementaires sur le terrain sont necessaires pour determiner s’il agit d’un individu
aberrant ou d une population de l’Amarante des rochers morphologiquement distincte.
Rock Firefinch Lagonosticta sanguinodorsalis
was recently described from the Jos Plateau,
central Nigeria (10°32’N 09o21’E), by Payne
(1998). Sightings were also reported from the
Mandara Mountains (11°02’N 13°44’E), c.500
km to the east (see Payne 1998, Borrow & Demey
2001, Fry & Keith 2004). In 2005, the species
was discovered in the Maroua area, northern
Cameroon, c.80 km south-east of the Mandara
Mountains (N. Borrow in Bull. ABC 12: 179).
Since then there have been several additional
sightings from northern Cameroon, where the
species is thought to be a locally common resident
(Mills 2010).
To gather more data on this species in the
Mandara Mountains, we visited this area on 9
October 2008. On the first day, we searched for
an access from the main road into the mountains.
While we passed through some farmland with
gallery forest, a pair of firefinches, calling like
Rock Firefinches, flew over. They landed in a
tree c. 10 m away and eventually flew down to
a stream, permitting good views. The male had
a deep red head, breast and belly, brown wings
and a grey bill. The male Rock Firefinch from
the Jos Plateau, with which we are familiar, has
a brownish-grey crown, a brownish-red back, a
deep red rump, and a black tail with red fringes to
the outer rectrices. The face down to the throat,
breast and belly is deep red, and the wings are dark
reddish brown. Other male firefinches with red
heads are Red-billed Firefinch L. senegala , which
has a red or pink, not grey, bill, and Black-bellied
Firefinch L. rara , which has a black, not red, belly.
The female, observed at a distance of c. 15 m, had
a brownish-grey head, brown wings and a grey
bill, i.e. similar to female Rock Firefinch from
Figures 1-2. Adult male Rock Firefinch Lagonosticta
sanguinodorsalis , Jos Plateau, 27 September 2004 (Martin
Stervander)
Amarante des rochers Lagonosticta sanguinodorsalis male
adulte, Plateau de Jos, 27 septembre 2004 (Martin
Stervander)
21 0 - Bull ABC Vol 17 No 2 (2010)
Rock Firefinch in the Mandara Mountains: Abalaka et al.
Figures 3-4. Adult male Rock Firefinch Lagonosticta
sanguinodorsalis, Gwoza, Mandara Mountains, 1 1
October 2008 (Keith Larson)
Amarante des rochers Lagonosticta sanguinodorsalis male
adulte, Gwoza, Monts Mandara, 1 1 octobre 2008 (Keith
Larson)
the Jos Plateau. The location was in a riparian
corridor through farmland converted from Guinea
savannah, at c.500 m altitude.
Next day, we erected mist-nets at the site and,
after two hours, trapped a male. Its plumage was
similar to that of a typical male Rock Firefinch,
except that it lacked the grey crown (Figs. 1-4).
In the hand, some small grey feathers on the
crown were visible, but the overall impression
was red, especially when seen at a distance. The
red also seemed to have a different shade, slightly
paler and less deep, than that of Rock Firefinch
from the Jos Plateau. Wing length was 55 mm
and weight 10.9 g, i.e. within the range ol the Jos
Plateau birds.
On the Jos Plateau, Rock Firefinch is usually
associated, as its name implies, with rocky habitats
(Wright & Jones 2005; pers. obs.), at altitudes
ranging from 750 m at Kagoro to 1,350 m at
Jos (Abalaka & Jones in prep.); in northern
Cameroon it has been recorded at 300—430 m (M.
Mills in lift. 2009).
The population in the Mandara Mountains
and neighbouring areas of Cameroon (pers. obs.)
may differ from Rock Firefinch described from
the Jos Plateau, although further investigation
is needed to reveal whether these differences are
consistent and warrant formal description as a
new taxon.
Acknowledgements
We thank the A. P. Leventis Ornithological Research
Institute for logistic support and for partly financing
this expedition. We also thank Martin Stervander for
photographs of Rock Firefinch from the Jos Plateau.
Ron Demey, Michael Mills and Bob Payne commented
on an earlier version of this note. This is contribution
no. 40 of the A. P. Leventis Ornithological Research
Institute.
References
Abalaka, J. 1. & Jones, P. J. In prep. Population densities
of the Rock Firefinch Lagonosticta sanguinodorsalis
and some other estrildine and viduine finches on
the Jos Plateau, Nigeria.
Borrow, N. & Demey, R. 2001. Birds of Western Africa.
London, UK: Christopher Helm.
Brandt, M. J. & Cresswell, W. 2008. Breeding
behaviour, home range and habitat selection in
Rock Firefinches Lagonosticta sanguinodorsalis in
the wet and dry season in central Nigeria. Ibis 150:
495-507.
Fry, C. H. & Keith, S. (eds.) 2004. The Birds of Africa.
Vol. 7. London, UK: Christopher Helm.
Mills, M. S. L. (2010) Rock Firefinch Lagonosticta
sanguinodoralis and its brood parasite, Jos Plateau
Indigobird Vidua maryae, in northern Cameroon.
Bull. ABC 17: 86-89.
Payne, R. B. 1998. Anew species of firefinch
from northern Nigeria and its association with the
Jos Plateau Indigobird Vidua maryae. Ibis 140:
368-381.
Wright, D. & Jones, P. 2005. Population densities
and habitat associations of the range-restricted
Rock Firefinch Lagonosticta sanguinodorsalis on
the Jos Plateau, Nigeria. Bird Conserv. Intern. 15:
287-295.
"A. P. Leventis Ornithological Research Institute, Jos,
Nigeria. E-mails: ilewigs@yahoo.com, ottosson@pt.lu,
talatutende@yahoo. com
b Dept, of Animal Ecology, Lund University, Sweden.
E-mail: keith. larson @zooekol. lu. se
Received 22 September 2009; revision accepted 26
November 2009.
Rock Firefinch in the Mandara Mountains: Abalaka et al.
Bull ABC Vol 17 No 2 (2010) -211
A record of brood parasitism of Barratt’s Warbler Bradypterus
barratti by African Emerald Cuckoo Chrysococcyx cupreus
Michael S. L Mills
Une donnee de parasitisme de la Bouscarle des fourres Bradypterus barratti par le Coucou foliotocol
Chrysococcyx cupreus. Le seul hote du Coucou foliotocol Chrysococcyx cupreus connu avec certitude en
Afrique australe est la Camaroptere a tete grise Camaroptera brachyura. L’auteur rapporte l’observation
de deux Bouscarles des fourres Bradypterus barratti adultes nourrissant un jeune Coucou foliotocol dans
la foret de Xumeni, KwaZulu-Natal, Afrique du Sud. Ceci constitue la premiere donnee de parasitisme
chez la Bouscarle des fourres, qui devient ainsi le deuxieme hote confirme du Coucou foliotocol en
Afrique australe.
At Xumeni Forest (29°55’S 29°51’E), near
Donnybrook, southern KwaZulu-Natal,
South Africa, on the afternoon of 7 January 2010,
I was drawn to the presence of a nearby Barratt’s
Warbler Bradypterus barratti by its loud, distinctive
song. Careful observation revealed two adults
feeding a begging nestling in dense undergrowth
beside the main track through the forest. The
young bird was significantly larger than the adults
and, based on its size, shape and barred plumage,
I identified it as a juvenile Chrysococcyx cuckoo. I
observed the two adult Barratt’s Warblers feeding
the young cuckoo for c. 2 minutes at a distance
of 5-10 m, at eye level. The underparts of the
cuckoo, including the throat, were whitish with
green bars, the crown had green markings, and
there were no pale markings on the head. These
features eliminated the possibility that the bird
was a juvenile Klaas’s Cuckoo C. klaas or Dideric
Cuckoo C. caprius (Chittenden 2005), and led to
my identification of the bird as a juvenile African
Emerald Cuckoo C. cupreus. During the course
of the afternoon I observed an adult male African
Emerald Cuckoo singing nearby, but no other
Chrysococcyx cuckoos.
In southern Africa the only proven host
of African Emerald Cuckoo is Green-backed
Camaroptera Camaroptera brachyura , although
several other small, insectivorous passerines are
suspected hosts (Chittenden 2005) and a wider
range of passerine hosts have been recorded
elsewhere in Africa (Irwin 1988, Payne 2005).
This observation makes Barratt’s Warbler only
the second confirmed host of African Emerald
Cuckoo in southern Africa, and the first member
of the genus Bradypterus , although Little Rush
Warbler B. baboecala is a known host of Dideric
Cuckoo (Squelch & Safe-Squelch 1994). This also
constitutes the first record of brood parasitism in
Barratt’s Warbler (Vernon & Dean 2005).
Acknowledgements
Ian Darling, Frank Hamilton, Ruaraidh Hamilton and
Stuart Housden shared this observation with me, and
Bob Payne commented on the manuscript.
References
Chittenden, H. N. 2005. African Emerald Cuckoo
Chrysococcyx cupreus. In Hockey, P. A. R., Dean,
W. R. J. & Ryan, P. G. (eds.) Roberts — Birds of
Southern Africa. Seventh edn. Cape Town: Trustees
of the John Voelcker Bird Book Fund.
Irwin, M. P. S. 1988. In Fry, C. H., Keith, S. & Urban,
E. K. (eds.) The Birds of Africa. Vol. 3. London,
UK: Academic Press.
Payne, R. B. 2005. The Cuckoos. Oxford: Oxford
University Press.
Squelch, P. & Safe-Squelch, W. 1994. Didric Cuckoo
being fed by Little Rush Warblers. East Afr. Nat.
Hist. Soc. Bull. 24: 39-40.
Vernon, C. J. & Dean, W. R. J. 2005. Barratt’s Warbler
Bradypterus barratti. In Hockey, P. A. R., Dean,
W. R. J. & Ryan, P. G. (eds.) Roberts— Birds of
Southern Africa. Seventh edn. Cape Town: Trustees
of the John Voelcker Bird Book Fund.
DST/NRF Centre of Excellence at the Percy FitzPatrick
Institute of African Ornithology, University of Cape
Town, Rondebosch 7701, South Africa; and Birding
Africa, 21 Newlands Road, Claremont 7708, Cape Town,
South Africa. E-mail: michael@birdingafrica. com
Received 19 January 2010; revision accepted 5 May
2010.
21 2 -Bull ABC Vol 17 No 2 (2010)
Brood parasitism of Barratt’s Warbler by African Emerald Cuckoo: Mills
First record of Streaky-breasted Flufftail Sarothrura boehmi
for Benin
Johannes Merz f and Sharon Merz?
Premiere mention du Rale de Bohm Sarothrura boehmi pour le Benin. Les 5 et 6 septembre 2009,
une femelle et deux juveniles du Rale de Bohm Sarothrura boehmi ont ete observes dans des champs de riz
a la peripherie de Cobly, au nord-ouest du Benin (10°28’N 01°01’E). Le chant a pu etre enregistre. Ceci
constitue la premiere donnee pour le Benin.
On 5-6 September 2009, we paid early-
morning visits to the north-eastern outskirts
of Cobly, in north-west Benin (10°28’N 01°01’E).
While standing on a bridge over a seasonally
swollen stream feeding adjacent rice fields, we
heard, on both days, between 07.30 and 08.00
hrs, a distinctive call coming from the nearest rice
paddy and a more distant field. It comprised a
series of 10—40 low whoo notes, initially slightly
rising, then, after the tenth note, remaining
constant in volume and pace, with c.2 seconds
between each whoo, and terminating in a few
less regularly uttered notes. Our sound-recording
proved to be virtually identical to that of male
Streaky-breasted Flufftail Sarothrura boehmi on
Chappuis (2000).
On the first day, after hearing the vocalisation,
we observed a small rail flying with dangling legs
from the rice paddy cA m from us and landing c. 3
m away. It was nicely lit by the morning sun: the
upper wings and short body were entirely dark
brown with pale mottling and streaking, and the
legs were dull greenish-yellow. On 6 September,
we observed the bird again under comparable
conditions, but this time it was joined by two
similar but sooty-grey birds, which flew up from
a nearby spot. The appearance of these three birds
fits the description of, respectively, female and
juvenile Streaky-breasted Flufftails (Borrow &
Demey 2001).
The female Red-chested Flufftail S. rufa , the
only other flufftail in West Africa (east to Nigeria)
which frequents similar habitat, is noticeably paler,
whereas juvenile White-spotted Flufftail S. pulchra
is considerably browner than the two juveniles
we observed (Borrow & Demey 2001). African
Crake Crex egregia and Black Crake Amaurornis
flavirostris are larger and possess different plumage
features and jizz.
We heard male Streaky-breasted Flufftails on
two further occasions: on 20 September 2009 at
Didani, cA km west of Cobly, and on 8 August
2009 at Landa-Pozanda (09°31’N 01°17’E), in
neighbouring Togo, where the species has not yet
been recorded (Cheke & Walsh 1996). Both sites
comprised partially flooded wooded savannah
near streams. On neither occasion were we able
to get close enough to see the birds or record their
vocalisations.
The distribution of Streaky-breasted Flufftail
is imperfectly known. This secretive species is
considered to be an intra-African migrant over
most of its range and is known to breed during
the rains at scattered localities, from south-east
Congo-Kinshasa and Kenya to Zimbabwe (Taylor
& van Perlo 1998). It is very rarely recorded
in West Africa, with only two records from
Nigeria, one off the coast of Guinea and an
unsubstantiated sight record in Mali (Urban et al.
1986, de Bont 2001, Borrow & Demey 2001).
Our record is thus the first for Benin, and it
seems that the species also occurs in neighbouring
Togo, although confirmation is preferably needed.
The presence of two juveniles in early September
suggests that egg laying occurred in June or July,
during the rainy season, and it seems that Streaky-
breasted Flufftail also breeds in West Africa.
Acknowledgements
We thank Patrick Claffey for encouraging us to submit
this note and Ron Demey and Franchise Dowsett-
Lemaire for assisting with references.
References
de Bont, M. 2001. Observations of Bohm’s Flufftail
Sarothrura boehmi in Nigeria. Malimbus 23:
65-66.
Borrow, N. & Demey, R. 2001. Birds of Western Africa.
London, UK: Christopher Flelm.
First record of Streaky-breasted Fluffail for Benin: Merz & Merz
Bull ABC Vol 17 No 2 (2010) -21 3
Chappuis, C. 2000. African Bird Sounds: Birds of
North , West and Central Africa and Neighbouring
Atlantic Islands. 15 CDs. Paris: Societe d’Etudes
Ornithologiques de France & London, UK: British
Library.
Cheke, R. A. & Walsh, J. F. 1996, The Birds of Togo:
An Annotated Check-list. BOU Check-lisr No. 14.
Thing: British Ornithologists’ Union.
Taylor, B. & van Perlo, B. 1998. Rails. A Guide to the
Rails , Crakes, Gallinules and Coots of the World.
Robertsbridge: Pica Press.
Urban, E. K„ Fry, C. H. & Keith, S. (eds.) 1986. The
Birds of Africa. Vol. 2. London, UK: Academic
Press.
“ B.P. 45, Tanguieta, Republic of Benin. E-mail: Johannes-
Sharon_Merz@sil. org
Received 7 October 2009; revision accepted 11 June
2010.
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214 -Butt ABC Vol 17 No 2 (2010)
First record of Streaky-breasted Fluff ail for Benin: Merz & Merz
First records of Ruddy Turnstone Arenaria interpres for Benin
Guy R. Manners
Premieres mentions du Tournepierre a collier Arenaria interpres pour le Benin. Le 1 fevrier 2010, un
Tournepierre a collier Arenaria interpres a ete observe sur la lagune de Cotonou, Benin. Le 5 fevrier, deux ou
trois oiseaux etaient presents au meme endroit. II s’agit des premieres donnees pour le pays de ce migrateur
palearctique, qui est commun ou peu commun le long de la cote ouest-africaine et a deja ete enregistre dans
les pays voisins, le Togo et le Nigeria.
On 1 February 2010, between 17.00 and
19.00 hrs, I was observing the birds near
the mouth ol the Cotonou lagoon, Benin, from
the terrace of the Hotel du Lac. My attention
was drawn to a small, stocky wader amongst the
nearest rocks a few hundred metres away. Despite
the rather bad light, coming from the west as
I was viewing south-west with lOx binoculars,
the bird’s dark brown upperparts combined with
the white underparts, brown throat and upper
breast, and rather short bill indicated that I was
watching a Ruddy Turnstone Arenaria interpres in
either non-breeding (winter) or juvenile plumage
(BirdGuides & Oxford University Press 2003—
06), a species with which I am familiar in the UK.
On the evening of 5 February, two or three Ruddy
Turnstones, showing the same features as the bird
on 1 February, were present at the same location.
All were either resting or possibly foraging on the
rocks; I did not see them in flight. Their size, shape
and distinctive plumage was confirmed by direct
comparison with nearby Common Sandpipers
Actitis hypoleucos. There are no serious contenders
as confusion species: Charadrius plovers are
smaller and even shorter billed and most Calidris
sandpipers are also smaller and have a different
jizz, while the larger species have longer bills.
Although Ruddy Turnstone has not yet been
reported from Benin (Dowsett 1993, Dowsett et
al. submitted), its occurrence is no surprise. It has
been recorded in neighbouring Nigeria (Elgood et
al. 1994) and Togo (Cheke & Walsh 1996), and
the species is a common to uncommon Palearctic
passage migrant and winter visitor to West African
coasts (Urban et al. 1986, van Gils & Wiersma
1996, Borrow & Demey 2001, Delany et al.
2009).
Acknowledgements
Patrick Claffey and Ron Demey commented on earlier
drafts ol this note and provided references.
References
BirdGuides & Oxford University Press. 2003-06. Birds
of the Western Palearctic Interactive 1.1. DVD-
ROM. Sheffield: BirdGuides.
Borrow, N. & Demey, R. 2001. Birds of Western Africa.
London, UK: Christopher Helm.
Cheke, R. A. & Walsh, J. F. 1996. The Birds of Togo:
An Annotated Check-list. BOU Check-list No. 14.
Tring: British Ornithologists’ Union.
Delany, S., Scott, D., Dodman, T. & Stroud, D.
(eds.) 2009. An Atlas of Wader Populations in
Africa and Western Eurasia. Wageningen: Wetlands
International.
Dowsett, R. J. 1993. Afrotropical avifaunas: annotated
country checklists. Benin. Tauraco Res. Rep. 5:
64-68.
Dowsett, R. J., Dowsett-Lemaire, F. & Claffey, P. M.
submitted. The avifauna of Benin: additions and
corrections. Bull. ABC.
Elgood, J. H., Heigham, J. B., Moore, A. M., Nason,
A. M., Sharland, R. E. & Skinner, N. J. 1994.
The Birds of Nigeria: An Annotated Check-list.
BOU Check-list No. 4. Second edn. Tring: British
Ornithologists’ Union.
van Gils, J. & Wiersma, P. 1996. Family Scolopacidae
(sandpipers, snipes and phalaropes). In del Hoyo,
J., Elliott, A. & Sargaral, J. (eds.) Handbook of
the Birds of the World. Vol. 3. Barcelona: Lynx
Edicions.
Urban, E. K., Fry, C. H. & Keith, S. (eds.) The Birds of
Africa. Vol. 2. London, UK: Academic Press.
25 Hi life Id, Foxton, Cambridgeshire CB22 6RZ, UK.
E-mail: guy@grmanners.com
Received 15 March 2010; revision accepted 2 May
2010.
First records of Ruddy Turnstone for Benin: Manners
Bull ABC Vol 17 No 2 (2010) -21 5
First record of Grey-necked Picathartes Picathartes oreas
for Central African Republic
Rod Cassidf,b, Barry Wat kin f and Tamar Cassidy
Premiere mention du Picatharte du Cameroun Picathartes oreas pour la Republique centrafricaine.
En novembre 2009, six nids du Picatharte du Cameroun Picathartes oreas ont ete decouverts sur des parois
rocheuses a l’interieur de la foret dense du Parc National de Dzangha Sangha, Republique centrafricaine.
Deux nids contenaient chacun deux oisillons; un adulte a ete observe. Ceci constitue la premiere donnee
pour le pays; la population nicheuse la plus proche se trouve a environ 1 40 km vers Pouest, dans le Parc
National de Boumba-Bek, au Cameroun.
On 16 November 2009, while exploring a
heavily forested area on the Sangha River, in
the south-western Central African Republic, RC
& BW found three nests consisting of half-cups of
mud plastered against a rock wall (Figs. 1-2). They
were obviously those of Grey-necked Picathartes
Picathartes oreas (Fry 2000). Two of the nests
Figure 1. Rock-face with nest of Grey-necked Picathartes
Picathartes oreas , Dzangha Sangha Protected Area, Central
African Republic, 16 November 2009 (R. Cassidy).
Paroi rocheuse avec nid du Picatharte du Cameroun
Picathartes oreas , Parc National de Dzangha Sangha,
Republique centrafricaine, 16 novembre 2009 (R.
Cassidy)
contained two chicks each; the third was damaged.
While observing the nests, an adult Grey-necked
Picathartes appeared, but did not stay long. A
week later, further exploration revealed another
three nests along a 500-m stretch of rock-face.
The site is c. 5 km upstream of Sangha Lodge,
near Bayanga in the Dzanga Sangha Reserve. The
area is covered in dense tropical forest and has
a large rocky ridge with exposed rock-faces and
waterfalls.
Grey-necked Picathartes is a local species
recorded from south-east Nigeria, Cameroon,
Equatorial Guinea and Gabon (Fry 2000), and
has recently also been reported from south-west
Congo-Brazzaville (Mamonekene & Bokandza-
Paco 2006). It has not previously been reported
from Central African Republic (Dowsett
1993, Thompson 2007). The nearest breeding
population is in Boumba-Bek National Park,
Figure 2. Nest of Grey-necked Picathartes Picathartes
oreas, Dzangha Sangha Protected Area, Central African
Republic, 16 November 2009 (R. Cassidy).
Nid du Picatharte du Cameroun Picathartes oreas , Parc
National de Dzangha Sangha, Republique centrafricaine,
16 novembre 2009 (R. Cassidy)
21 6 - Bull ABC Vol 17 No 2 (2010)
First record of Grey-necked Picathartes for Central African Republic: Cassidy et al.
Cameroon (02°40’N 15°00’E), c. 140 km to the
west (R. J. Dowsett & F. Dowsett-Lemaire in
Bull. ABC 5: 142; Taku Awa II pers. comm.). We
are hoping to conduct further field work in the
Sangha Lodge area to assess the range and size of
this population. Further updates will be posted at
www.sanghalodge.com.
Acknowledgements
We thank Gregory Davies for his help with the drafting
ol this note and Ron Demey for his comments and help
with references.
References
Dowsett, R. J. 1993. Afrotropical avifaunas: annotated
country checklists. Central African Republic.
Tauraco Res. Rep. 5: 168-175.
Fry, C. H. 2000. Family Picarthartidae. In Fry, C.
H. & Keith, S. (eds.) The Birds of Africa. Vol. 6.
London, UK: Academic Press.
Mamonekene, V. & Bokandza-Paco, F. L. 2006.
Premiere observation du Picatharte du Cameroon
Picathartes oreas au Congo-Brazzaville. Bull. ABC
13: 84-85.
Thompson, H. S. S. 2007. Family Picathartidae
(picathartes). In del Floyo, J., Elliott, A. & Christie,
D. A. (eds.) Handbook of the Birds of the World. Vol.
12. Barcelona: Lynx Edicions.
a Silver Safaris, 267 Stead Avenue, Queenswood, Pretoria,
South Africa. E-mail: rod@silversafaris. com
b Sangha Lodge, Bayanga, Central African Republic.
‘ BirdSection, Vertebrate Department, Transvaal Museum,
PO Box 413, Pretoria, South Africa. E-mail: tamar@nfi.
museum
Received 20 January 2010; revision accepted 11 May
2010.
First record of Chilean Skua Catharacta chilensis
for the African region
Peter G. Ryan
Premiere mention du Labbe du Chili Catharacta chilensis pour la region africaine. Un Labbe du
Chili Catharacta chilensis a ete photographie a ’tie Inaccessible, dans l’archipel de Tristan da Cunha, dans
l’Atlantique Sud, en novembre 2009. L'espece niche le long de la cote de l’Amerique du Sud, du centre du
Chili jusqu’au sud de FArgentine. Les oiseaux non nicheurs se dispersent vers le nord jusqu’au Perou et le
Bresil, et occasionnellement atteignent les Malouines, mais la donnee presentee ici constitue apparemment
la premiere en dehors des eaux continentales sud-americaines.
The taxonomy of the large, Catharacta skuas
breeding in the Southern Flemisphere is far
from resolved. Even comparison of mitochondrial
markers has failed to elucidate the situation,
with only partial segregation of the various taxa
(Ritz et al. 2008). This is perhaps unsurprising
given records of hybridisation among taxa (e.g.,
Devilliers 1978, Reinhardt et al. 1997). However,
most authorities recognise three species: South
Polar Skua C. maccormicki, Subantarctic Skua
C. antarctica and Chilean Skua C. chilensis
(Furness 1996, Olsen & Larsson 1997). Of these,
Subantarctic Skua is resident in the African region,
with breeding populations ol C. a. lonnbergii
on the subantarctic Prince Edward and Crozet
archipelagos, and Tristan Skua C. a. hamiltoni is
endemic to Tristan da Cunha and Gough Island.
South Polar Skua is a scarce non-breeding migrant
to African waters. To date, there have been no
records of Chilean Skuas in the African region.
In November 2009, I photographed a Chilean
Skua on Inaccessible Island, in the Tristan da
Cunha group, central South Atlantic Ocean. It
was first observed on 25 November and remained
until at least 1 December, when I left the island.
During this period it loosely associated with a
non-breeding ‘club’ of Tristan Skuas roosting at
Skua Pond, near West Point, but it also attempted
to advertise a territory on the adjacent Scirpus-
covered bog, where c.20 pairs of Tristan Skuas
First record of Grey-necked Picathartes for Central African Republic: Cassidy et al.
Bull ABC Vol 17 No 2 (2010) -217
Figure 1. Chilean Skua Catharacta chilensis showing
cinnamon vent and rather small bill with bluish base,
Skua Pond, Inaccessible Island, Tristan da Cunha,
November 2009 (Peter Ryan)
Labbe du Chili Catharacta chilensis, Skua Pond, lie
Inaccessible, Tristan da Cunha, novembre 2009 (Peter
Ryan). Noter le bas-ventre cannelle et le bee relativement
petit a base bleuatre.
Figure 3. Chilean Skua Catharacta chilensis in flight,
showing the compact jizz and rather small, neatly-defined
white wing flashes, Inaccessible Island, Tristan da Cunha,
November 2009 (Peter Ryan)
Labbe du Chili Catharacta chilensis en vol, lie
Inaccessible, Tristan da Cunha, novembre 2009 (Peter
Ryan). Noter la forme compacte et les taches alaires
blanches relativement petites et bien definies.
Figure 2. Chilean Skua Catharacta chilensis (left) with
typical adult Tristan Skua C. antarctica hamiltoni,
Inaccessible Island, Tristan da Cunha, November 2009
(Peter Ryan)
Labbe du Chili Catharacta chilensis (a gauche) avec un
Labbe de Tristan C. antarctica hamiltoni adulte typique,
ile Inaccessible, Tristan da Cunha, novembre 2009
(Peter Ryan)
Figure 5. Chilean Skua Catharacta chilensis giving the
long-call display on the floating mat of Scirpus sulcatus
on Skua Pond, Inaccessible Island, Tristan da Cunha,
November 2009 (Peter Ryan)
Labbe du Chili Catharacta chilensis, emettant le long cri
de parade sur un tapis flottant de Scirpus sulcatus, Skua
Pond, lie Inaccessible, Tristan da Cunha, novembre 2009
(Peter Ryan)
breed. It was less approachable than the local
Tristan Skuas and was frequently chased by them.
The Chilean Skua was readily distinguished from
the rather variable local skuas by its paler face and
neck with prominent golden hackles, contrasting
with the dark eye-patch and breast. At close
range, its paler bill with a dark tip was visible.
The bird was also slightly smaller, with a more
compact appearance, especially in flight, recalling
South Polar Skua. Although its body was washed
rufous, it was not as richly coloured as many
Chilean Skuas, but in flight it clearly showed the
distinctive cinnamon underwing-coverts. When
the bird displayed, its long-call was distinctly
deeper and more hoarse than that of the Tristan
Skuas, sounding almost goose-like.
The most likely confusion is with the Northern
Hemisphere Great Skua C. skua , which is more
richly coloured than Subantarctic or South Polar
Skuas. Great Skuas show considerable variation in
plumage, but R. Furness (in lift. 2009), who has
studied Great Skuas for 30 years, commented that
21 8 -Bull ABC Vol 17 No 2 (2010)
First record of Chilean Skua from the African region: Ryan
Figure 4. Chilean Skua Catharacta chilensis landing
on Skua Pond, Inaccessible Island, Tristan da Cunha,
November 2009, showing the diagnostic cinnamon
underwing-coverts (Peter Ryan). Note also the distinctive
paler buff tips to the uppertail-coverts.
Labbe du Chili Catharacta chilensis , aterrissant sur Skua
Pond, He Inaccessible, Tristan da Cunha, novembre 2009
(Peter Ryan). Noter les couvertures sous-alaires brun clair
diagnostiques et les pointes chamois clair des couvertures
sus-caudales.
‘no Great Skua I’ve seen has had as strongly ginger-
coloured underwing-coverts as this bird’. The
only other possibility is that the bird is of hybrid
origin. Chilean Skuas apparently hybridise with
both Falkland Skuas C. a. antarctica (Devilliers
1978) and South Polar Skuas (Reinhardt et al.
1997), but hybrids usually appear intermediate in
plumage and structure (Devilliers 1978), whereas
this bird is typical of a Chilean Skua in worn
plumage.
Chilean Skuas breed along the coast of South
America from central Chile to southern Argentina,
with non-breeders dispersing north as far as
Peru and Brazil (Olsen & Larsson 1997). They
occasionally reach the Falkland Islands, but this
appears to be the first record of a Chilean Skua
away from South American continental waters.
Acknowledgement
I thank Bob Furness for useful comments on the
identity of this bird.
References
Devilliers, P. 1978. Distribution and relationships of
South American skuas. Gerfaut 68: 374-417.
Furness, R. W. 1996. Family Stercorariidae (skuas).
In del Hoyo, J., Elliott, A. & Sargatal, J. (eds.)
Handbook of the Birds of the World. Vol. 3.
Barcelona: Lynx Edicions.
Olsen, K. M. & Larsson, FI. 1997. Skuas and Jaegers:
A Guide to the Skuas and Jaegers of the World.
Robertsbridge: Pica Press.
Reinhardt, K., Blechschmidt, K., Peter, H.-U. &
Montalti, D. 1997. A hitherto unknown
hybridization between Chilean and South Polar
Skua. Polar Biol. 17: 114-118.
Ritz, M. S., Millar, C., Miller, G. D., Phillips, R. A.,
Ryan, P. G., Sternkopf, V., Liebers-Helbig, D. &
Peter, Fd-U. 2008. Phylogeography of the southern
skua complex — rapid colonisation of the Southern
Hemisphere during a glacial period and reticulate
evolution. Mol. Phyl. & Evol. 49: 292-303.
Percy FitzPatrick Institute, University of Cape Town,
Rondebosch 7701, South Africa. E-mail: peter. ryan@uct.
ac.za
Received 28 December 2009; revision accepted 30
April 2010.
First record of Chilean Skua from the African region: Ryan
Bull ABC Vol 17 No 2 (2010) -21 9
Photospot:
Observations du Faucon concolore Falco concolor dans les
environs d’Antananarivo, Madagascar
Bruno Boedts
Observations of Sooty Falcon Falco concolor around Antananarivo, Madagascar. A small group of
2-8 Sooty Falcons Falco concolor was observed hunting at the end of the rainy season in waste lands at
Ivandry, a residential area in northern Antananarivo, from 28 February to 4 April 2009. Immatures were
more numerous at the end of the period than at the beginning. During the midday hours, Sooty Falcons
preyed on large non-flying insects such as Coleoptera taken on low plants. Prey was then consumed quickly
in flight or sometimes on a perch. In 2006-09, numbers of Sooty Falcons, a Near-Threatened species,
did not decrease appreciably at Ivandry. They are apparently undisturbed by human activities, which are
limited at this site.
A Madagascar, le Faucon concolore Falco
concolor, espece quasi-menacee qui niche en
Afrique du nord-est et sur la Peninsule arabique,
est present de la fin octobre jusqu’a la mi-mai
sur l’ensemble de file, du niveau de la mer
jusqu’a 1.500 m (Orta 1994, Langrand 1995,
BirdLife International 2008). Pendant quatre
annees consecutives, de 2006 a 2009, j’ai observe
des Faucons concolores dans le quartier residentiel
d’lvandry (47°31’E 1 8°5 1 S), situe en banlieue
nord de la capitale Antananarivo sur les hauts
plateaux malgaches (1.266 m). En 2009, un
groupe de 2-8 individus frequentant un site
de chasse a ete photographie au cours de douze
visites etalees sur plus d’un mois, du 28 fevrier
au 4 avril. A Madagascar, les insectes constituent
une tres grande majorite des proies de cette
espece, dont le regime alimentaire change de fa<;on
drastique entre les sites de reproduction, oil elle se
nourrit principalement de passereaux, et les sites
d’hivernage (Ferguson-Lees & Christie 2001).
A Ivandry, l’espece est vue chaque annee a
partir de la fin janvier, la date la plus precoce (21
janvier) ayant ete notee en 2007. Les Faucons
concolores frequentent plusieurs endroits autour
de la plaine inondee de Laniera d une superficie
de plusieurs milliers d’hectares, cultivee sur une
grande partie pour la production de riz. Ils
utilisent un site pour le repos et un autre pour la
chasse. Le site de repos favori, oil un ou plusieurs
individus peuvent generalement etre observes en
debut de journee, est un grand pin dans un jardin
prive, dominant le sud de la plaine et a proximite
de blocs d’immeubles a appartements, autour
desquels les faucons sont souvent aperqus en vol.
Le site de chasse, qui se trouve a environ 1 km
du site de repos, comprend des terrains en friche
partiellement cultives (vieilles vignes, legumes,
arbres fruitiers tels que bananiers) et des paturages
pour bovins d’une superficie estimee a 20 ha
sur un plateau dont un cote donne sur la plaine
non cultivee a cet endroit, et fautre sur le village
d’Androhibe. Des poteaux metalliques ou en bois
d’environ 8 m de haut se trouvent au bord des
chemins ou au milieu des terrains (Fig. 1).
En 2009, un groupe de Faucons concolores
etait present chaque jour sur le site de chasse.
Les adultes sont arrives les premiers et ont ete
progressivement rejoints par des immatures, a
partir du 14 mars. Differentes formes d’immatures,
caracterisees par la blancheur du ventre et des
joues, ainsi que la couleur grise ou brune du
dos, ont ete photographiees (Figs. 2-5). Pendant
la deuxieme quinzaine de mars, la proportion
d’immatures par rapport aux adultes s’est stabilisee
a quatre pour deux.
Durant ces observations, les Faucons concolores
etaient poses le plus souvent sur les poteaux ou
les fils electriques d’ou ils pouvaient observer les
alentours, ou sur des branches d’arbres, parfois
situees a moins de 3 m du sol, pour se reposer ou
nettoyer leur plumage pendant de longs moments
(Fig. 6). Les faucons sont habitues a certains
perchoirs ou ils sont vus a chaque observation.
Aucune pelote de rejection n’a ete trouvee au pied
de ces perchoirs. Ils ne sont generalement pas
deranges par une presence humaine meme tres
proche et n’attirent pas specialement l’attention
220 -Bull ABC Vol 17 No 2 (2010)
Pbotospot: Sooty Falcon in Madagascar
des habitants. Les faucons se tiennent le plus
souvent a moins de 100 m l’un de l’autre. Pendant
la nuit, ils dorment en haut de grands arbres, a une
vingtaine de metres de hauteur.
Les perchoirs sont egalement utilises par le
Faucon de Newton F. newtoni. Lorsque des
Faucons concolores se rapprochent trop pres de
cette espece, celle-ci peut les deloger. II arrive
que deux Faucons concolores se poursuivent en
vol pendant quelques instants ou qu’ils tournent
autour d’autres oiseaux comme des pigeons
domestiques, sans les attraper. En milieu de
journee, les Faucons concolores peuvent se poser
a terre sur un sol dur degage pour etaler leurs ailes
au soleil. Ils peuvent aussi utiliser les courants
thermiques pour s’elever en Fair et ensuite planer
sans un battement d’aile vers un autre endroit. Un
rassemblement plus important d’une quinzaine
d’individus tournant et s’elevant dans le del a
ainsi ete vu en mars 2006 au dessus du quartier
d’Analamahitsy, une zone urbaine d’Antananarivo
situee a environ 2 km d’lvandry. Des oiseaux
solitaires ont egalement ete vus a d’autres endroits
aux environs du nord d’Antananarivo tels que
Ilafy et Ivato, respectivement situes a environ 4 et
10 km d’lvandry.
Pendant les heures chaudes de la journee,
environ entre 09.00 et 16.00 heures, les Faucons
concolores s’adonnent par vent faible, a la chasse
aux insectes se trouvant dans la vegetation
basse, notamment des Coleopteres cetoines
(Cetoniinae), qui pullulent a cet endroit en fin
de saison des pluies comprise entre novembre
et avril. A Ivandry, le Faucon concolore n’est
done pas specifiquement crepusculaire comme
parfois indique dans la litterature (Kemp &
Kemp 1998). De son perchoir, il s’envole en
plongeant pour chasser en rase motte les insectes
poses dans la vegetation (Fig. 7). Ceux-ci sont
attrapes rapidement avec les serres dirigees en
avant (Fig. 8). La capture d’insectes volants n’a
pas ete observee durant ces periodes de chasse
intensive. Elle a toutefois ete vue a la fin avril 2009
sur un Faucon concolore immature chassant seul
au site de chasse. L’insecte en vol etait capture a
une hauteur d’une vingtaine de metres. Une fois
capture, l’insecte est maintenu dans les serres,
decortique avec le bee et ingurgite en quelques
secondes, soit le plus souvent en vol, dans 80%
des observations, tout en continuant a planer a
moins de 10 m du sol pendant quelques instants
(Fig. 9), soit, pour certains faucons habitues a
cette technique, sur un perchoir habituel, ou
l’insecte est maintenu contre une surface (Fig. 10).
Les parties tendres de l’insecte sont extraites et la
cuticule rejetee. Un Faucon concolore peut ainsi
se nourrir d’un grand nombre d’insectes en un
temps reduit. Lorsque les insectes sont manges en
vol, les periodes de chasse pratiquees en groupe de
deux ou trois dans le meme secteur durent 10-15
minutes, pendant lesquelles une dizaine d’insectes
sont captures par faucon. Les oiseaux ratent
rarement leur proie. Apres une periode de chasse,
ils se reposent pendant une quinzaine de minutes
avant de reprendre leur vol. Lorsque le temps est
nuageux, ils restent immobiles pendant de longs
moments sur leur perchoir ou se mettent dans un
endroit plus cache. Contrairement aux Guepiers
de Madagascar Merops superciliosu;, les faucons
n’ont pas ete vus en train de chasser au dessus de
la plaine inondee. Cependant a quelques reprises
en fin de journee, un faucon solitaire a ete vu en
vol bas au dessus de la plaine. Les Guepiers de
Madagascar, egalement abondants a cette periode
de l’annee, se nourrissent generalement, au niveau
de ce site, d’autres types d’insectes que ceux
chasses par les Faucons concolores, tels que les
Odonates toujours captures lorsque ces insectes
sont en vols.
A la fin de l’hivernage, l’ensemble des Faucons
concolores disparait d’un jour a l’autre du site de
chasse. En 2009, le depart a correspondu avec le
passage du cyclone Jade les 6-8 avril. Neanmoins,
des immatures ou adultes solitaires pouvaient
encore etre vus jusqu’au 25 avril aux sites de repos
et de chasse.
La conservation des Faucons concolores
dans des sites d’hivernage semi urbains comme
celui d’lvandry ne requiert pas de mesures
speciales vu qu’ils s’accommodent de milieux
degrades et sont peu deranges par la presence de
l’homme. L’abondance d’insectes est cependant
cruciale. De ce fait, la menace la plus serieuse
est constitute par revolution de 1’agriculture. Si
celle-ci s’industrialisait, certains amenagements
ou certaines pratiques culturales telles que
l’utilisation de pesticides risqueraient d’engendrer
une diminution du nombre d’insectes et par
voie de consequence une diminution du nombre
de Faucons concolores. De plus, bien que ce
ne soit pas le cas a Ivandry, leur familiarite et
visibilite risqueraient de les exposer au braconnage,
Photospot: Sooty Falcon in Madagascar
Bull ABC Vol 17 No 2 (2010) - 221
222 -Bull ABC Vol 17 No 2 (2010)
Figure 1. Site de chasse : vue des terrains en friche et de la
plaine au fond. Poteau servant de poste d’observation a un
Faucon concolore Falco concolor (B. Boedts)
Sooty Falcon Falco concolor hunting area: view over the
study area with the flooded plain behind. The post was
used as a lookout (B. Boedts)
Figure 2. Faucon concolore Falco concolor immature a
ventre clair, dos gris et cou clair (B. Boedts)
Immature Sooty Falcon Falco concolor with pale belly, grey
back and pale neck (B. Boedts)
Figure 3. Faucon concolore Falco concolor immature a
ventre fonce, dos gris et cou fonce (B. Boedts)
Immature Sooty Falcon Falco concolor showing the dark
belly, grey back and dark neck (B. Boedts)
Figure 4. Faucon concolore Falco concolor immature a
ventre clair, dos brun et cou clair (B. Boedts)
Immature Sooty Falcon Falco concolor with pale belly,
brown back and pale neck (B. Boedts)
Figure 5. Faucon concolore Falco concolor immature a
ventre fonce, dos gris et cou clair (B. Boedts)
Immature Sooty Falcon Falco concolor with dark belly, grey
back and pale neck (B. Boedts)
Figure 6. Faucon concolore Falco concolor adulte au repos
(B. Boedts)
Perched adult Sooty Falcon Falco concolor (B. Boedts)
Figure 7. Faucon concolore Falco concolor adulte chassant
en rase motte (B. Boedts)
Hunting adult Sooty Falcon Falco concolor (B. Boedts)
Figure 8. Faucon concolore Falco concolor adulte capturant
un insecte pose (B. Boedts)
Adult Sooty Falcon Falco concolor capturing a non-flying
insect (B. Boedts)
Figure 9. Faucon concolore Falco concolor adulte
decortiquant un insecte en vol (B. Boedts)
Adult Sooty Falcon Falco concolor consuming an insect in
flight (B. Boedts)
Figure 10. Faucon concolore Falco concolor adulte pose
decortiquant un insecte (B. Boedts)
Adult Sooty Falcon Falco concolor consuming an insect
while perched (B. Boedts)
Bull ABC Vol 17 No 2 (2010) - 223
notamment a des Fins de taxidermie marchande,
comme pratique dans la region de l’ltasy (L.-A.
Rene de Rolland comm. pers.).
Pendant les quatre annees d’observation,
le nombre de Faucons concolores n’a pas
sensiblement diminue. Leur arrivee a Ivandry
se fait relativement tard dans la saison, en Fin
janvier, indiquant qu’ils doivent visiter avant cela
d’autres regions de Madagascar plus seches que
les hauts plateaux. Ils restent nombreux a Ivandry
jusqu’a debut avril d’ou ils partent probablement
directement rejoindre leurs lieux de nidification
pour y arriver des la Fin avril ou en mai (Orta
1994).
Remerciements
Je remercie Lily-Arison Rene de Rolland, Olivier
Langrandet Jean-Marc Thiollay pour leurs commentaires
sur une premiere version de Particle, ainsi que Julien
Ramananpamonjy pour ses encouragements a publier
Farticle.
References
BirdLife International. 2008. Species lactsheet : Falco
concolor. www.birdlife.org (consulte le 11 avril
2009).
Ferguson-Lees, J. & Christie, D. A. 2001. Raptors of the
World. London, UK: Christopher Helm.
Orta, J. 1994. Sooty Falcon Falco concolor. En del
Hoyo, J., Elliott, A. & Sargatal, J. (eds.) Handbook
of the Birds of the World. Vol. 2. Barcelona : Lynx
Edicions.
Kemp, A. & Kemp, M. 1998. Sasol Birds of Prey of
Africa and its Islands. London, UK : New Holland.
Langrand, O. 1995. Guide des Oiseaux de Madagascar.
Lausanne & Paris : Delachaux et Niestle.
BP 1718, Analakely, Antananarivo 101, Madagascar.
E-mail : boedtsbruno@yahoo.fr
Requ le 4 mai 2009 ; revision acceptee le 25 novembre
2009.
224 - Bull ABC Vol 17 No 2 (2010)
Photospot: Sooty Falcon in Madagascar
Photospot:
A breeding island for Lesser Flamingos Phoeniconaias minor
at Kamfers Dam, Kimberley, South Africa
Mark D. Anderson " and Tania A. Andersonh
Une lie pour Flamants nains Phoeniconaias minor a Kamfers Dam, Kimberley, Afrique du Sud. La
construction d une lie speciale a Kamfers Dam, pres de Kimberley en Afrique du Sud, en 2006, afin d’inciter
des Flamants nains Phoeniconaias minor a y nicher, a connu un succes surprenant. Jusqu’a 80.000 flamants
etaient present et 13.000 jeunes sont arrives a l’envol en une seule saison. En 2009/10, F augmentation du
niveau d eau a malheureusement cause l’echec de la reproduction dans la plus grande partie de la colonie.
II est toutefois prevu de reparer les degats afin d’accroitre l’attrait de File pour les flamants. Kamfers Dam
pourrait devenir un des sites les plus importants au monde pour cette espece Quasi Menacee.
Kamfers Dam is a 500-ha perennial wetland
located just north of Kimberley, South
Africa. This wetland was previously an ephemeral
pan, but is now permanently inundated as it
receives most of Kimberley’s effluent water. It
also receives storm-water run-off from Kimberley
and from a c. 160 krrr large catchment. Kamfers
Dam probably supports the largest permanent
population of Lesser Flamingos Phoeniconaias
minor in southern Africa, with sometimes >80,000
individuals present.
During September 2006, following months
of planning and a protracted Environmental
Impact Assessment process, a flamingo island was
constructed by Ekapa Mining at Kamfers Dam.
The construction was a massive undertaking,
with more than 26,000 tons of material being
moved. The cost of construction was an estimated
half a million rand (c.UK£45,000). Within two
weeks of the 200-m causeway being removed, the
first Lesser Flamingos made use of the island for
roosting purposes. Within a few months r.30,000
Figure 1. Kamfers Dam, prior to the island’s construction, with the city of Kimberley visible in the background (Mark
D. Anderson)
Kamfers Dam avant la construction de File, avec la ville de Kimberley en arriere-plan (Mark D. Anderson)
Figure 2. The S-shape limits the area of the island exposed to water and wind erosion, and the two sheltered bays
permit the flamingos easy access to the island. The island was constructed mainly of calcrete, from a nearby quarry, but
was also topped with a 20-cm layer of clay (providing material for the flamingos to construct their nests). Four large
ponds were constructed on the island, fed by water from a pump submerged in the dam and powered by solar panels.
The causeway was removed once the island construction was completed (Mark D. Anderson)
L’ile a la forme dun S, limitant ainsi la surface exposee a Ferosion par Faction de l’eau et du vent, et les deux baies
abritees facilitent Faeces des flamants. L’ile a ete construite principalement avec du calcrete provenant d'une carriere
proche, auquel une couche d’argile de 20 cm a ete ajoutee (fournissant ainsi aux flamants le materiau pour la
construction des nids). Quatre grands etangs ont ete commits sur 1 ile, remplis d eau par une pompe submergee et
actionnee par des panneaux solaires. La route d’acces a ete enlevee des que la construction de File fut terminee (Mark D.
Anderson)
Photospot: Lesser Flamingos at Kamfers Dam, Kimberley, South Africa
Bull ABC Vol 17 No 2 (2010) - 225
Photospot: Lesser Flamingos at Kamfers Dam, Kimberley, South Africa
226 -Bull ABC Vol 17 No 2 (2010)
Figure 3. The island, covered with Lesser Flamingos
Phoeniconaias minor, is clearly visible from commercial
plane flights between Johannesburg and Cape Town. The
large ponds can be seen at the bottom half of the island,
and the high-lying area (specifically constructed as an
escape area for small chicks should the dam’s water level
rise) at the top left (Mark D. Anderson)
L’ile, couverte de Flamants nains Phoeniconaias minor ,
esr clairement visible a partir des vols commerciaux
de Johannesbourg a Cape Town. Les grands etangs se
trouvent dans la moitie inferieure de file et la zone elevee
(qui a ete construite specifiquement pour permettre aux
poussins d’echapper le cas echeant aux eaux montantes)
en haut a gauche (Mark D. Anderson)
Figure 4. During the 2006/7 summer, the Lesser
Flamingos Phoeniconaias minor constructed 160 nests and
laid eggs, but the breeding event was unsuccessful (Mark
D. Anderson)
Pendant Fete 2006/7, les Flamants nains Phoeniconaias
minor ont consrruit 160 nids et pondu, mais la tentative
de reproduction a echouee (Mark D. Anderson)
Lesser Flamingos were roosting on the island at
night, with many birds also using the island during
the day. Despite nest construction and egg laying,
the 2006/07 breeding attempt was unsuccessful.
Figure 5. At the end of the 2007/8 breeding event, there
were more than 7,000 nests on the island, increasing to
c. 10,000 after the 2008/9 breeding event. During winter
2007, a webcam (‘FlamCam’) was installed; images can be
can be viewed at www.africam.com (Mark D. Anderson)
En 2007/8, il y avait plus de 7.000 nids sur File, tandis
qu en 2008/9 le nombre avait augmente jusqu’a environ
10.000. Pendant l’hiver de 2007, un webcam a ete
installe (Mark D. Anderson). Les images du ‘FlamCam’
peuvent etre visionnees sur www.africam.com (Mark D.
Anderson)
Figure 6. A series of high-resolution images of the
island was taken on a monthly basis from a helicopter
during one fly-over at an altitude of c.200 m (Mark
D. Anderson). There was no visible disturbance to the
flamingos. The images were imported into Photoshop
and, using a sheep-counter, the total numbers of eggs,
chicks, incubating adults, and adults were counted.
Une serie d’images a haute resolution a ete prise chaque
mois a partir d’un helicoptere survolant File a une hauteur
d’environ 200 m (Mark D. Anderson). Les flamants ne
semblaient pas etre deranges. Les images ont ete importees
dans Photoshop et le nombre d'oeufs, de poussins et
d’adultes en train de couver ou non, a ete compte.
Figure 7. The first chicks were observed on 2 January
2008, with the breeding success being a historic event for
Lesser Flamingo Phoeniconaias minor conservation (Mark
D. Anderson). The chicks seemed to leave their nests 3-4
days after hatching, then remain in the vicinity of the
nests for a short period (perhaps a week), before joining
the large creches.
Les premiers poussins ont ete observes le 2 janvier 2008,
la reproduction constituant un evenement historique pour
la protection du Flamant nain Phoeniconaias minor (Mark
D. Anderson). Les poussins semblaient quitter leur nid
apres 3-4 jours et ensuite rester pres du nid pendant une
courte periode (peut-etre une semaine), avant de rejoindre
les grandes creches.
Figure 8. A group of immature Lesser Flamingos
Phoeniconaias minor that fledged from the island (Mark
D. Anderson)
Un groupe de jeunes Flamants nains Phoeniconaias minor
nes sur File (Mark D. Anderson)
Figures 9—10. Lesser Flamingos Phoeniconaias minor bred
successfully on the island during 2007/8 and 2008/9,
producing an estimated 9,000 and 13,000 chicks,
respectively (Mark D. Anderson)
Les Flamants nains Phoeniconaias minor ont niche sur File
avec succes en 2007/8 et 2008/9, produisant environ 9.000
et 13.000 poussins, respectivement (Mark D. Anderson)
Subsequently, for about four months during
2007, no flamingos used the island.
The Lesser Flamingos returned to the island in
large numbers in September 2007 when breeding
Photospot: Lesser Flamingos at Kamfers Dam, Kimberley, South A frica
Bull ABC Vol 17 No 2 (2010) - 227
displays were observed. On 2 January 2008,
the first chicks were seen and, by April 2008,
it was estimated that 9,000 chicks had hatched
during that summer’s breeding event. The Lesser
Flamingos bred again in 2008/09, this time
producing an estimated 13,000 chicks.
The 2009/10 breeding event started a month
earlier, in early September 2009, but rising water
levels and then heavy rains during early November
2009 resulted in the loss of probably >1,000
chicks and an unknown number of eggs, and the
flooding of about three-quarters of the island. It
is estimated that c.7,500 nests were destroyed by
the rising waters. In early January 2010, the island
was still flooded and only c.500 Lesser Flamingo
chicks fledged.
The breeding of Lesser Flamingos at Kamfers
Dam represents (a) the first time that the species
has bred on an artificial structure, (b) the first-
ever successful breeding event in South Africa, (c)
the third breeding locality in southern Africa, (d)
the fourth breeding locality in Africa, and (e) the
sixth breeding locality globally (Anderson 2008,
Childress et al. 2008). In addition to Kamfers
Dam, Lesser Flamingos only breed at Etosha Pan
in Namibia, Sua Pan in Botswana, Lake Natron in
Tanzania and at the Zinzuwadia and Purabcheria
salt pans in north-west India (Anderson 2008,
Childress et al. 2008).
Importantly, the Lesser Flamingos have bred
at Kamfers Dam during three successive summers,
whilst at other localities they nest less frequently
(for example they are successful every ten years at
Etosha Pan: Simmons 1996).
Kamfers Dam, the breeding island, and the
dam’s flamingos currently face several important
threats, including: (a) rising water levels
(through an increased inflow of sewage water),
(b) deteriorating water quality (for the same
reason) and (c) the development of Northgate, a
massive housing development (comprising 6,500
middle-class homes) on the property adjoining
Kamfers Dam. The Save the Flamingo Association
(www.savetheflamingo.co.za), Kamfers Dam’s
landowners (the Booth family), BirdLife South
Africa, and the Wildlife & Environment Society of
South Africa are addressing these threats through
various means, including litigation.
With various anthropogenic threats at the
Lesser Flamingo’s other breeding sites (problems
in their catchments, soda ash plants, etc.), Kamfers
Dam could become increasingly important lor
the conservation of the Lesser Flamingo, which
is considered Near Threatened globally. It is
anticipated that global warming will result in less
frequent inundation (and therefore less frequent
breeding) at the other breeding sites (especially
Etosha Pan and Sua Pan), making the potentially
more stable regime at the artificial Kamfers Dam
of even greater importance.
Ekapa Mining has committed to rebuilding
the island, which will mean re-constructing the
200-m causeway and raising the height of the
island, but only once the dam’s water level
stabilises and when the Sol Plaatje (Kimberley)
Municipality can deal with the excess water and
treat the sewage water to an acceptable quality.
Acknowledgements
The island was constructed by Ekapa Mining, and Jahn
Hohne and Peter Hohne’s contributions in particular are
very gratefully appreciated. Kamfers Dam’s landowners,
Herbert & Brenda Booth, are very supportive of this
important conservation project. Barney Horwitz, Helen
Dagut and Terry Winstanley have provided expert legal
assistance. The FlamCam (webcam) was sponsored by
Ekapa Mining and Nedbank. Brooks Childress, Alan
Johnson, Arnaud Bechet, Warwick Tarboton and
Rob Simmons have provided useful inputs during the
project. The Save the Flamingo Association has actively
campaigned for the conservation of Kamfers Dam and
its flamingos.
References
Anderson, M. D. 2008. A vision in pink. Lesser
Flamingo breeding success. Africa — Birds &Birding
13(2): 42-49.
Childress, B., Nagy, S. & Hughes, B. (compilers) 2008.
International Single Species Action Plan for the
Conservation of the Lesser Flamingo ( Phoeniconaias
minor). CMS Tech. Ser. 18 & AEWA Tech. Ser.
34. Bonn.
Simmons, R. E. 1996. Population declines, viable
breeding areas and management options for
flamingos in southern Africa. Conserv. Biol. 10:
504-514.
" BirdLife South Africa, PO Box 515, Randburg 2125,
South Africa. E-mail: director@birdlife.org.za
b McGregor Museum, PO Box 316, Kimberley 8300,
South Africa.
Received 25 December 2009; revision accepted 19
May 2010.
Photospot: Lesser Flamingos at Kamfers Dam, Kimberley, South Africa
228 -Bull ABC Vol 17 No 2 (2010)
Birding Rwanda — in search of Red-collared Babbler
Kupeornis rufocinctus , Albertine Rift endemics and more
Callan Cohen"1’, Peter Ryanb, Marcell Claasenc and Claver Ntoyinka!1
Observer les oiseaux au Rwanda— a la recherche du Phyllanthe a collier roux Kupeornis rufocinctus
et es especes endemiques du Rift albertin. Cet article presente deux des meilleurs sites pour observer
es oiseaux au Rwanda : la foret de Nyungwe (ou Ton peut trouver 25 des 35 especes endemiques du Rift
a bertin) et le Parc National de 1 Akagera (oil 525 especes d’oiseaux ont ete recensees, dont le Bec-en-sabot
du Nil Balaeniceps rex et plusieures especes confinees au bassin du Lac Victoria).
The tiny country of Rwanda is perched on
Central Africa’s Albertine Rift highlands,
straddling the watershed between the continent’s
two great rivers, the Nile and the Congo. It has
been largely overlooked by birders, who instead
are lured by the well-publicised bird diversity
and tourist facilities boasted by its northern
neighbour, Uganda. However, one of Africa’s
most charismatic and enigmatic birds, the Red-
collared Babbler Kupeornis rufocinctus, is only
accessible in Rwanda, as is Albertine Owlet
Glaucidium albertinum, and other species such
as Red-faced Barbet Lybius rubrifacies, Ruaha’
Chat Myrmecocichla ( arnotti ) collaris, Grauer’s
Swamp Warbler Bradypterus graueri, Kungwe
Apalis Apalis ( rufogidaris ) argentea and Purple-
breasted Sunbird Nectarinia purpureiventris are
perhaps most accessibly found here.
This article focuses on the two top strategic
birding areas, which are the largest remaining
blocks of natural habitat in this densely cultivated
country. Nyungwe National Park is the undoubted
jewel in the crown and is covered in most detail
here. One of the largest montane forests in Africa,
it has more Albertine Rift endemic birds than
any other site outside Congo-Kinshasa (see Table
1), and is easily accessed by an excellent tarmac
road. On the other side of the country, Akagera
National Park offers a broad diversity of savannah
and wetland birds, including Shoebill Balaeniceps
rex and several species conhned to the Lake
Victoria basin.
Focusing on these areas, it is quite possible
to record over 300 species in just ten days in
Rwanda, less than half the country’s total list of
almost 700 species. Most tourists visit during the
main dry season in June-September, although the
shorter December— January dry season may also
prove to be a rewarding time to visit. With the
1994 genocide now firmly in the past, Rwanda
is one of the most organised countries in Africa
and is proactively rebuilding its infrastructure and
promoting tourism. A bird atlas project has also
recently been initiated.
Albertine Rift Endemics
The forests of the western or Albertine Rift
support more endemic birds than any other
Endemic Bird Area in Africa. Adding to their
allure, some of Africa’s most enigmatic birds
occur here: Congo Bay Owl Phodilus prigoginei,
Prigogine’s Nightjar Caprimulgusprigogineiand
Schouteden’s Swift Schoutedenapus schoutedeni
are cumulatively known from fewer than ten
specimens! Extending patchily through eastern
Congo-Kinshasa, western Tanzania, Burundi,
Rwanda and Uganda, the Albertine Rift forests
support at least 35 strict endemics. Many of
these forests are under threat, especially due to
clearance for agriculture, and the status of those
forests in Congo-Kinshasa, which support the
greatest diversity of endemics, is poorly known.
In recent years, most birders ‘chasing’ the
Albertine Rift specialties have visited Uganda’s
Bwindi region, but this offers only a subset
of the region’s endemics. Rwanda’s Nyungwe
National Park offers a greater diversity in a
magnificent setting.
Nyungwe National Park
Nyungwe is one of Africa’s best forests for birding:
an excellent road runs through the national
park offering excellent vistas and chances for
25 of the 35 strict Albertine Rift endemics
(see Table 1). Nyungwe harbours all of the
Albertine Rift endemics recorded from Bwindi
in Uganda with the exception ol African Green
Birding Rwanda: Cohen et al.
Bull ABC Vol 17 No 2 (2010) - 229
Table 1. Endemic birds of the Albertine Rift.Taxa not recognised
specifically by the African Bird Club checklist are denoted by their
subspecies epithets. Chapin’s Flycatcher is listed here but is not a
strict Albertine Rift endemic as it also occurs at one site in Kenya.
Ruwenzori Nightjar Caprimulgus ruwenzorii is not listed as it is now
recognised to occur widely outside this region. Species occurring in
more than three forests in Congo-Kinshasa are coded simply DRC.
Tableau 1. Oiseaux endemiques du Rift albertin. Les taxons qui
ne sont par reconnus comme especes sur la liste de I'African Bird
Club sont indiques par le nom de la sous-espece en question. Le
Gobemouche de Chapin Muscicapa lendu est liste ici, bien qu’il ne soit
pas endemique au Rift albertin, puisqu'il se trouve egalement sur un site
au Kenya. L’Engoulevent du Ruwenzori Caprimulgus ruwenzorii n’est
pas mentionne, car Ton sait maintenant qu'il est largement distribue
en dehors de la region. Les especes qui se trouvent dans plus de
trois forets au Congo-Kinshasa sont indiquees simplement par DRC.
Handsome Francolin Francolinus nobilis
Nyungwe
Ruwenzori Turaco Ruwenzorornis johnstoni
Nyungwe
Congo Bay Owl Phodilus prigoginei
Itombwe, DRC
Albertine Owlet Glaucidium albertinum
Nyungwe
Prigogine's Nightjar Caprimulgus prigoginei
Itombwe, DRC
Dwarf Honeyguide Indicator pumilio
Nyungwe
African Green Broadbill Pseudocalyptomena graueri
Kivu & Itombwe, DRC;
Bwindi, Uganda
Grauer’s Cuckooshrike Coracina graueri
DRC
Prigogine’s Greenbul Chlorocichla prigoginei
Lendu Plateau, DRC
Archer's Robin Chat Cossypha arched
Nyungwe
Red-throated Alethe Alethe poliophrys
Nyungwe
Kivu Ground Thrush Zoothera (piaggiae) tanganjicae
Nyungwe
Neumann's Warbler Hemitesia neumanni
Nyungwe
Grauer's Swamp Warbler Bradypterus graueri
Nyungwe
Grauer’s Warbler Graueria vittata
Nyungwe
Chapin’s Crombec Sylvietta (leucophyrus) chapini
Lendu Plateau, DRC
Red-faced Woodland Warbler Phylloscopus laetus
Nyungwe
Ruwenzori Apalis Apalis ruwenzorii
Nyungwe
Mountain Masked Apalis Apalis personata
Nyungwe
Kabobo Apalis Apalis ( porphyrolaema ) kaboboensis
Mount Kabobo, DRC
Kungwe Apalis Apalis ( rufogularis ) argentea
Nyungwe
Yellow-eyed Black Flycatcher Melaenornis ardesiacus
Nyungwe
Chapin’s Flycatcher Muscicapa lendu
DRC, Bwindi Uganda
and Kakamega Kenya;
unconfirmed for
Nyungwe
Ruwenzori Batis Batis diops
Nyungwe
Red-collared Babbler Kupeornis rufocinctus
Nyungwe
Chapin's Babbler Kupeornis chapini
DRC
Stripe-breasted Tit Parus fasciiventer
Nyungwe
Blue-headed Sunbird Cyanomitra alinae
Nyungwe
Purple-breasted Sunbird Nectarinia purpureiventris
Nyungwe
Ruwenzori Double-collared Sunbird Cinnyris stuhlmanni Nyungwe
Regal Sunbird Cinnyris regius
Nyungwe
Rockefeller’s Sunbird Cinnyris rockefelieri
DRC; unconfirmed for
Nyungwe
Yellow-crested Helmetshrike Prionops alberti
DRC
Strange Weaver Ploceus alienus
Nyungwe
Dusky Crimsonwing Cryptospiza jacksoni
Nyungwe
Shelley’s Crimsonwing Cryptospiza shelleyi
Nyungwe
Legends to figures on opposite page
Figure 1. Ruwenzori Turaco Ruwenzorornis johnstom
(Callan Cohen / www.birdingafrica.com). This Albertine
Rift endemic is easily seen at Nyungwe.
Touraco du Ruwenzori Ruwenzorornis johnstoni (Callan
Cohen / www.birdingafrica.com). Cec endemique du Rift
albertin est facile a voir a Nyungwe.
Figure 2. Nyungwe forest is the best place to see Purple-
breasted S unbird Nectarinia purpureiventris (Callan
Cohen / www.birdingafrica.com)
La foret de Nyungwe est le meilleur site pour observer le
Souimanga a ventre pourpre Nectarinia purpureiventris
(Callan Cohen / www.birdingafrica.com)
Figure 3. Neumann’s Warbler Hemitesia neumanni lurks
in Nyungwe’s dark understorey (Callan Cohen / www.
birdingafrica.com)
Le Crombec de Neumann Hemitesia neumanni frequence
le sous-bois de Nyungwe (Callan Cohen / www.
birdingafrica.com)
Figure 4. Grauer’s Swamp Warbler Bradypterus graueri,
Kamiranzovu swamp, Nyungwe National Park (Peter
Ryan)
Bouscarle de Grauer Bradypterus graueri, marais de
Kamiranzovu, Parc National de Nyungwe (Peter Ryan)
Figure 5. Rwanda is the best place to obverve the social
Red-collared Babbler Kupeornis rufocinctus (Ray Tipper)
Le Rwanda est le meilleur endroit pour observer le
Phyllanthe a collier roux Kupeornis rufocinctus (Ray
Tipper)
Figure 6. Ruwenzori Apalis Apalis ruwenzorii inhabits
tangles on Nyungwe’s forest edge (Callan Cohen / www.
birdingafrica.com)
L’Apalis du Ruwenzori Apalis ruwenzorii occupe les
feuillages denses des lisieres de la foret de Nyungwe
(Callan Cohen / www.birdingafrica.com)
Broadbill Pseudocalyptomena graueri (and
given the broadbill’s unobtrusive nature, it may
well occur, as large parts of Nyungwe seem
superficially similar to Ruhiza in Bwindi where
the broadbill occurs). When birding in Nyungwe
one has a sense of exploration; that anything could
appear over the next hill. For example, the rare
Owl-faced Monkey Cercopithecus hamlyni was
only discovered in Nyungwe in 1989. Chapin’s
Flycatcher Muscicapa lendu and Rockefeller’s
Sunbird Cinnyris rockefelleri have been claimed
from Nyungwe, but their occurrence requires
confirmation, and the secretive Congo Bay Owl
Phodilus prigoginei may also occur.
Target birds. — 25 Albertine Rift endemics
including Albertine Owlet, Neumann’s Warbler
230 -Bull ABC Vol 17 No 2 (2010)
Birding Rwanda: Cohen et al.
Birding Rwanda: Cohen et al.
Bull ABC Vol 17 No 2 (2010) - 231
232 - Bull ABC Vol 17 No 2 (2010)
Birding Rwanda: Cohen et al.
Legends to figures on opposite page
Figure 7. Red-faced Woodland Warbler Phylloscopus
laetus forms part of canopy bird parties at Nyungwe
National Park (Callan Cohen / www.birdingafnca.com)
Le 1 ouillot a lace rousse Phylloscopus laetus fait partie des
rondes insectivores de la canopee dans le Parc National de
Nyungwe (Callan Cohen / www.birdmgafrica.com)
Figure 8. Cinnamon-chested Bee-eater Merops oreobates
occurs on the edge of highland forest clearings (Callan
Cohen / www.birdingafrica.com)
Le Guepier montagnard Merops oreobates se trouve a
la lisiere des clairieres a haute altitude (Callan Cohen /
www.birdingafrica.com)
Figure 9. The almost mythical Albertine Owlet
Glaucidium albertinum has been mist-netted in this patch
ol mossy forest near Kamiranzovu swamp, Nyungwe
National Park (Callan Cohen / www.birdingafnca.com)
La Chevechette du Graben Glaucidium albertinum a ete
capturee au filet japonais dans ce lambeau de foret pres
du marais de Kamiranzovu, Parc National de Nyungwe
(Callan Cohen / www.birdingafrica.com)
Figure 10. Northern Double-collared Sunbird Cinnyris
reichenoivi is common and widespread in Nyungwe
National Park (Peter Ryan)
Le Souimanga de Preuss Cinnyris reichenowi est commun
et repandu dans le Parc National de Nyungwe (Peter
Ryan)
Figure 11. Liihder’s Bushshrike Laniarius luehderi skulks
in tangles at mid and lower elevations (Callan Cohen /
www.birdingafrica.com)
Le Gonolek de Luhder Laniarius luehderi frequence la
vegetation dense a moyenne et basse altitude (Callan
Cohen / www.birdingafrica.com)
Figure 12. Papyrus Gonolek Laniarius mufumbiri occurs
in the extensive papyrus swamps of Akagera National
Park (David Winter)
Le Gonolek des papyrus Laniarius mufumbiri se rencontre
dans les papyraies du Parc National de l’Akagera (David
Winter)
Figure 13. L'Hoest’s Monkey Cercopithecus Ihoesti can be
seen on the roadside in Nyungwe (Callan Cohen / www.
birdingafrica.com)
Le Cercopitheque de l’Hoest Cercopithecus Ihoesti peut
etre observe le long de la route qui traverse Nyungwe
(Callan Cohen / www.birdingafrica.com)
Figure 14. Ruwenzori Batis Batis diops favours the lower
and mid levels in the forest of Nyungwe National Park
(Callan Cohen / www.birdingafrica.com)
Le Pririt du Ruwenzori Batis diops frequente les strates
basses et moyennes de la foret de Nyungwe (Callan
Cohen / www.birdingafrica.com)
Hemitesia neumanni, Grauer’s Swamp Warbler,
Red-collared Babbler and Purple-breasted
Sunbird.
Habitats. — Nyungwe encompasses almost
1,000 km2 of montane forest and heaths at
1,600-2,950 m elevation.
Getting there. — Situated in the south-west of
the country on the border with Burundi, the park
takes about 3-4 hours to reach on mostly good tar
roads from Kigali.
Top birding areas. (1) Roadside birding. — The
main road between Butare and Cyangugu runs
through the park for 55 km and the undulating
terrain boasts spectacular scenery, with unbroken
forest stretching into the hazy distance. It also
facilitates birding, with opportunities to observe
canopy species at eye-level on the steeper slopes.
Soaring raptors to look for include African Cuckoo
Hawk Aviceda cuculoides , African Harrier Hawk
Polyboroides typus, African Goshawk Accipiter
tachiro , Mountain Buzzard Buteo oreophilus,
Cassin’s Spizaetus africanns and Ayres’s Hawk
Eagles Hieraaetus ayresii and Crowned Eagle
Stephanoaetus coronatus.
A host of the commoner Albertine Rift endemics
can be found in the roadside tangles at the forest
edge including Ruwenzori Apalis ruwenzorii and
Mountain Masked Apalises A. personata , Yellow-
eyed Black Flycatcher Melaenornis ardesiacus,
Ruwenzori Batis Batis diops, and Blue-headed
Cyanomitra alinae and Regal Sunbirds Cinnyris
regius. One of the more interesting endemics
is Grauer’s Warbler Graueria vittata , the sole
member of its genus. This rather secretive, dull
grey bird of dense tangles and creepers is best
located by its soft trilling call, which is remarkably
similar to that of a Scaly-throated Honeyguide
Indicator variegatus. The sweet warbles ol African
Hill Babbler Pseudoalcippe abyssinica emanate
from these tangles too. Tambourine Dove Turtur
tympanistria, Olive Thrush Turdus olivaceus,
Collared Sunbird Hedydipna collaris and African
Yellow White-eye Zosterops senegalensis are
common.
Great Blue Turaco Coiythaeola cristata is
commonly seen from the road and the forest
rings to the raucous calls of Black-billed Turaco
Tauraco schuettii. Nyungwe must be one of the
best places to see the bizarre Ruwenzori Turaco
Ruwenzorornis johnstoni, which possesses an
atypical, squirrel-like call and is placed in its
Birding Rwanda: Cohen et al.
Bull ABC Vol 17 No 2 (2010) - 233
own genus. Also in the treetops are Waller’s
Onychognathus walleri, Slender-billed 0.
temiirostris, Stuhlmann’s Poeoptera stuhlmanni
and Sharpe’s Starlings Pholia sharpii. Scan from
the valley viewpoints for these species, as weli
as for African Olive Pigeon Columba arquatrix
and Black-and-white-casqued Hornbill
Bycanistes subcylindricus, whilst the calls of Barred
Long-tailed Cuckoo Cercococcyx montanus
and Yellow-rumped Pogoniulus bilineatus and
Western Green Tinkerbirds P. coryphaeus ring
out below.
Nyungwe is rich in bushshrikes, with Doherty’s
Bushshrike Telophorus dohertyi and Mountain
Sooty Boubou Laniarius poensis common in
tangles throughout, and Liihder’s Bushshrike
Laniarius luehderi at lower elevations. Higher
in the tangles, watch out for the buff-breasted
morph ol Many-coloured Bushshrike Telophorus
midticolor, which is confined to the southern
Albertine Rift, and Yellowbill Ceuthmochares
aereus. Look out too in these higher tangles
and the canopy for Chestnut-throated Apalis
porphyrolaema, Grey A. cinerea and Black-
throated Apalises A. jacksoni.
Chubb’s Cisticola Cisticola chubbi, Yellow-
bellied Estrilda quartinia and Black-headed
Waxbills E. atricapilla and Streaky Seedeater
Serinus striolatus are common in disturbed open
areas along the roadsides, where Cinnamon-
chested Bee-eater Merops oreobates, White-eyed
Slaty Melaenornis fischeri and African Dusky
Flycatchers Muscicapa adusta can be seen hawking
and Black Saw-wing Psalidoprocne pristoptera
is common. Most of the understorey ‘skulkers’
are most easily seen along the trails described
later, but it might be worth noting that we have
observed Grey-winged Robin Chat Cossypha
polioptera along the main road at 02°48.672”S
29°13.373”E.
After dark, Ruwenzori Nightjar Caprimulgus
ruwenzorii can be seen along the road, while
African Wood Owl Strix woodfordu and, with
some luck, Fraser’s Eagle Owl Bubo poensis can
be heard.
(2) U wink a (02°47.8 67”S 29°20.066”E;
parking lot adjacent to the headquarters). — There
is a wonderful network of trails through the forest,
centred on the park headquarters at Uwinka.
Canopy birding will be further enhanced with the
construction of a canopy walkway at Uwinka due
to be completed in late 2010, and plans are afoot
to erect canopy towers at other strategic sites.
The short walk from the parking to the reception
can be a good area to spot commoner Albertine
Rift endemics, including Red-faced Woodland
Warbler Phylloscopus laetus and Ruwenzori Batis,
and look out for Handsome Francolin Francolinus
nobilis on the edges of the road at dawn and dusk
(the francolin occurs widely throughout the forest
but is more easily heard than seen). Red-collared
Babbler actually occurs quite widely in Nyungwe
and has been seen along the forest trails here
too, but is more reliable on the Bigugu Trail (see
below).
(3) Bigugu trail (02°47.362”S 29°23.964”E;
start of the trail at the road). — The trail that
leads to Mount Bigugu, the highest point in
Nyungwe, is one of the best sites in the world
for Red-collared Babbler. Nyungwe is the
only forest outside Congo-Kinshasa where this
gorgeous species occurs, and like White-throated
Mountain Babbler Kupeornis gilberti of south-
west Cameroon, it roves through the forest in
small family groups, gleaning insects among
epiphytes on large branches. Parties maintain
contact with soft churrs, which can become
a harsh babbler-like cacophony in excitement.
The babblers are often associated with canopy
flocks also comprising Narina’s Apaloderma
narina and Bar-tailed Trogons A. vittatum,
White-headed Woodhoopoe Phoeniculus bollei,
Tullberg’s Woodpecker Campethera tullbergi,
Grey Cuckooshrike Coracina caesia. Eastern
Mountain Greenbul Andropadusnigriceps, Yellow-
streaked Greenbul Phyllastrephus flavostriatus,
Chinspot Batis Batis molitor (a canopy species in
Nyungwe), Stripe-breasted Tit Parus fasciiventer,
Lagden’s Bushshrike Malaconotus lagdeni and
Montane Oriole Oriolus percivali. Denser tangles
shelter Yellow-whiskered Greenbul Andropadus
latirostris, White-browed Crombec Sylvietta
leucophrys and Grauer’s Warbler.
Some of the most exciting species occur in
the understorey: listen out for White-starred
Robin Pogonocichla stellata, Equatorial Akalat
Sheppardia aequatorialis , Archer’s Robin Chat
Cossypha archeri (with its distinctive, tremulous
call), Red-throated Alethe (the latter especially at
ant swarms) and Mountain Illadopsis Illadopsis
pyrrhoptera. Dusky Crimsonwing Cryptospiza
jacksoni may flush from the forest path at the edges
234 - Bull ABC Vol 17 No 2 (2010)
Birding Rwanda: Cohen et al.
Primates of Nyungwe
Nyungwe is also well known for its primates
with 1 1 diurnal species present. Chimpanzee
Pun t) oglodytes occurs throughout and can be
searched ior here or at the nearby lower altitude
Cyamudongo Forest. The Uwinka area is
famous for its large troop of some 400 Angola
Pied Colobus Colobus ungolensis rwenzori.
Nyungwe must be one of the best places to see
l’Hoest’s Monkey Cercopithecus Ihoesti, which
is often present along roadsides. Also watch for
Grey-cheeked Mangabey Cercocebus albigena
johnstoni , Blue Monkey Cercopithecus mitis
doggetti, Mona Monkey C. mona, Red-tailed
Monkey C. ascanius schmidti , Vervet Monkey
C. (, aethiops ) pygerythrus and Olive Baboon
Papio anubis. Golden Monkey Cercopithecus
mitis kandti and Owl-faced Monkey C.
hamlyni are shy and little-known residents,
mainly found in the bamboo zone and seldom
seen. Note that Eastern Gorilla Gorilla beringei
no longer occurs here and is best searched for
at Volcanoes National Park, which also hosts
a selection of Aibertine Rift endemics and lies
on the northern border adjacent to Mgahinga
National Park in Uganda.
of clearings anywhere, but more luck is required
to find its much more elusive relative, Shelley’s
Crimsonwing C. shelleyi. Dense scrub at the edge
of clearings is inhabited by the vocal Cinnamon
Bracken Warbler Bradypterus cinnamomeus,
Mountain Yellow Warbler Chloropeta similis and
Banded Prinia Prinia bairdii.
(4) Kamiranzovu Marsh (02°48.897”S
29°16.011”E; start of the trail, and 02°48.582”S
29015.271”E; main marsh). — A trail leads down
to this spectacular marsh, which extends over
13 km2 in a valley bottom and supports a large
population of the localised and threatened
Grauer’s Swamp Warbler. This rare warbler is
easily seen here, drawing the attention by virtue
of its low whirring display-flight. The picturesque
forest surrounding the marsh literally drips with
epiphytes and there have been several sightings
of the almost mythical Aibertine Owlet here.
Listen too for Red-chested Owlet Glaucidium
tephronotum, which is widespread at Nyungwe
and often attracts mobbing groups of small
birds. Some of Africa’s most desired understorey
‘skulkers’ occur here too: listen out for Kivu
Ground Thrush Zoothera ( piaggiae ) tanganjicae,
the unique short-tailed Neumann’s Warbler and
Grey-chested Illadopsis Kakamega poliothorax.
Strange Weaver Ploceus alienus occurs in the
tangles here (and elsewhere in the forest), noisily
investigating clusters of leaves.
(5) Karamba area (02°47.882”S 29°11.168”E;
start of trail). — This level trail leads through quite
open forest and forest edge and has many of the
roadside species mentioned earlier, although it
is worth checking canopy flocks for Kungwe
Apalis especially, and White-bellied Robin Chat
Cossyphicida roberti can be found in the first
patch of forest. The incredibly iridescent Purple-
breasted Sunbird breeds at the forest edge here.
Open areas are worth checking for Scarce Swift
Schoutedenapus myoptilus and musing about the
possibility of the very similar Schouteden’s Swift
S. schoutedeni.
(6) Rangiro Road (02°47.672”S 29°20.590”E;
start of the road, 02°47.577”S 29°20.732”E; huge
Symphonia tree, and 02°47.672”S 29°20.590”E;
start of lower altitude forest). — Much of the
lower elevation forest has been replaced by tea
plantations, but some remains below Uwinka
and a rough but driveable road leads through
these remnants. Near the start of the descent,
a huge Symphonia tree (flowers reliably in July)
attracts many sunbirds including regular Purple-
breasted Sunbird. Dwarf Honeyguide Indicator
pumilio has been recorded here too. In the lower
forest patch, there is less of a montane ‘feel’
to the birding, and species include Elliott’s
Woodpecker Dendropicos elliotii, Shelley’s
Greenbul Andropadus masukuensis, Dusky Tit
Parus funereus , White-breasted Negrofinch
Nigrita fusconotus and Yellow-breasted Hyliota in
the forest canopy. The shy Shelley’s Crimsonwing
has been seen here, but can be found anywhere in
the park.
(7) Uwasenkoko Marsh (02°52.857”S
29°35.297”E). — This small, high-altitude marsh
spans the main road and is certainly the most
accessible place to see Grauer’s Swamp Warbler.
Red-chested Flufftail Sarothrura rnfa can be
heard ‘hooting’ from the dense grass. In the
surrounding shrublands, Brown Woodland
Warbler Phylloscopus umbrovirens and Ruwenzori
Double-collared Sunbird occur. Don’t be
misled by the smaller Northern Double-collared
Birding Rwanda: Cohen et al.
Bull ABC Vol 17 No 2 (2010) - 235
Sunbird Cinnyris reichenowi, which occurs
throughout much of the park and is especially
common around the guesthouse at Gisakura.
Recommended guides include. — Claver
Ntoyinka.
Recommended accommodation.— More
accommodation is planned, but for now there
are two guesthouses at Gisakura (one on a private
tea estate) and it is also possible to stay in one of
the many hotels in Cyangugu, on the shores of
Lake Kivu, and commute just over an hour to the
forest. Camping is possible at Uwinka.
Akagera National Park
With some 525 species, Akagera formerly boasted
one of the largest bird lists of any protected
area in Africa. However, more than half the
park was degazetted in 1997 to accommodate
returning refugees, a pattern that is likely to
be repeated more widely across Africa as other
countries inevitably begin to experience the
same phenomenal population densities and land
pressures operating in Rwanda. However, the
remaining area of park is still close to 1,100 knr
and offers great birding. Widespread savannah
and wetland birds dominate the area’s avifauna,
but there are a few more localised species, making
the park a great compliment to the montane forest
birding of Nyungwe.
Top birds. — Shoebill, Ring-necked
Francolin Francolinus streptophorus, Red-faced
Barbet, ‘Ruaha’ Chat, White-winged Swamp
Warbler Bradypterus carpalis, Miombo Wren
Warbler Calamonastes undosus, Tabora Cisticola
Cisticola angusticauda , Papyrus Gonolek Laniarius
mufumbiri.
Habitats. — A diversity of lowland habitats,
ranging from vast swamps and lakes on the
Akagera floodplain, through riparian thickets, dry
forest and woodland, to grassy plains and rocky
hills.
Getting there. — Situated on Rwanda’s eastern
border with Tanzania, Akagera is a three-hour
drive from Kigali (mostly on tarmac roads). Given
the relatively rough tracks through much of the
reserve, it requires several days to explore the more
remote northern parts of the park.
Top birding areas. ( 1 ) Final section of dirt
road before the park (01°97.869”S 30°58.030”E;
‘Ruaha’ Chat, and 01°96.255”S 30°58.981”E;
river crossing). — Once you leave the tarmac road,
numerous widespread savannah birds can be found
in the degraded woodland and agricultural areas.
Probably most interesting is the so-called ‘Ruaha’
Chat, the local taxon of White-headed Black
Chat Myrmecocichla arnotti , which Glen et al. (in
press) argue should be afforded species status due
to its genetic distinctness and the diagnostic white
cheeks and collar in the female. Unlike White-
headed Black Chat, which prefers natural miombo,
this chat is common around small villages and
breeds in the roofs of houses. Entering the more
pristine grassy broadleaf woodlands of the park,
it is replaced by Sooty Chat M. nigra. White-
collared Oliveback Nesocharis ansorgei has been
recorded at a river crossing and Miombo Wren
Warbler in denser bush at the park entrance.
(2) Slopes below Akagera Lodge (01°87.922”S
30°70.960”E). — Akagera Lodge is sited atop a
rocky ridge overlooking Lake Ihema and its
grounds teem with many woodland birds. Red-
faced Barbet can be seen in fruiting trees here,
and should also be searched for in the grassy
woodlands below the lodge. Rocky ridges support
small numbers of the scarce and reclusive Ring-
necked Francolin, which is best separated from
the more widespread Shelley’s Francolinus shelleyi.
Red-winged F. levaillantii and Coqui Francolins
F. coqui , and Red-necked Spurfowl F. afer by its
peculiar call. Tabora Cisticola, Souza’s Shrike
Lanius souzae and Orange-winged Pytilia Pytilia
afra have been recorded in these woodlands too.
(3) Lake Ihema (01°88.228”S 30“73.823”E).—
The shores of this vast lake support a huge
diversity of birds, not only in the grassy edges but
also the taller forest flanking the shores.
{4) Papyrus swamp (01°82.885”S
30°74.336”E). — This is an excellent spot for
White-winged Swamp Warbler, Carruther’s
Cisticola Cisticola carruthersi and Papyrus
Gonolek, all which skulk in the large papyrus
swamps here (be mindful of African Buffalo
Syncerus cajfer). Papyrus Canary Serinus koliensis
also occurs, but the curiously localised Papyrus
Yellow Warbler Chloropeta gracilirostris is
surprisingly absent from the park list. It is,
however, found at other wetlands in Rwanda,
including Rugezi Marsh in the north and at least
two marshes south of Kigali.
(5) Shoebill scanning point at Lake Birengero
(01°81.507”S 30°74.230”E). — The park has a
small resident population of Shoebills, but access
236 - Bull ABC Vol 17 No 2 (2010)
Birding Rwanda: Cohen et al.
to their swamps is restricted to a few vantage
points, and it is a matter of luck whether any are
visible. We recommend scanning the far edges of
the lake at this point. The area is apparently very
difficult to reach by boat because the lake is too
shallow.
Recommended guides include. — James
Muhizi.
Recommended accommodation. — Options
are limited, but Akagera Lodge offers upmarket
and very well-sited accommodation.
Acknowledgements
The Rwanda Tourism Board sponsored much of our
travel costs in Rwanda, and many of our observations
were shared with Rainer Summers, Glen Valentine
and Ray Tipper. The last-named is also thanked
for permission to publish his Red-collared Babbler
photograph.
Bibliography
Dowsett, R. J. (ed.) 1990. Survey of the Fauna and Flora
ofNyungwe Forest , Rwanda. Tauraco Res. Rep. 3.
Liege: Tauraco Press.
Glen, R., Bowie, R. C. K., Stolberger, S. & Voelker,
G. in press. Geographically structured plumage
variation among populations of White-headed
Black Chat ( Myrmecocichla arnotti) in Tanzania
confirms the race collaris to be a valid taxon. J.
Ornithol.
Offut, K., Masozera, M. & Gill, E. undated. Nyungwe
National Park Guide. Kigali: Nyungwe Forest
Conservation Project & New York: Wildlife
Conservation Society.
Plumptre, A. J., Masozera, M., Fashing, P. J., McNeilage,
A., Ewango, C., Kaplin, B. A. & Liengola, I. 2002.
Biodiversity Surveys of the Nyungwe Forest Reserve
in S.W. Rwanda. WCS Working Papers 18. New
York: Wildlife Conservation Society.
Stattersfield, A. J., Crosby, M. J., Long, A. J. & Wege,
D. C. 1998. Endemic Bird Areas of the World:
Priorities for Biodiversity Conservation. Cambridge,
UK: BirdLife International.
Vande weghe, J. P. 1 990. Akagera: Land of Water, Grass
and Fire. Brussels: WWF.
‘ Birding Africa, www.birdingafrica.com. E-mail: callan@
birdingafrica
bDST/NRF Centre of Excellence at the Percy FitzPatrick
Institute of African Ornithology, University of Cape
Town, Rondebosch 7701, South Africa.
c PO Box 181, Musanze, Rwanda.
d ORTPN, PO Box 7, Gikongoro, Rwanda.
Received 26 June 2010.
Birding Rwanda: Cohen et al.
Bull ABC Vol 17 No 2 (2010) - 237
www.birdingafrica.com
Rwanda
ABC Conservation Fund Tour
23 - 30 July 201 1 (8 days)
Bird Nyungwe Forest & Akagera:
Africa’s Albertine Rift Endemics hotspot
combined with one of Africa’s most
diverse parks.
Target Red-collared Babbler, Shoebill,
Red-faced Barbet, Purple-breasted Sunbird
& up to 25 Albertine Rift Endemics.
Optional Mountain Gorilla extension.
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Phone +27 21 531 91 48
238 -Bull ABC Vol 17 No 2 (2010)
Advertisement
Recent Reports
These are largely unconfirmed
records published for interest only;
records are mostly from late 2009
and early 2010, with a few from
earlier dates. We thank all birders
who have sent in their records and
urge them to submit full details to
the relevant national or regional
organisations. It is suggested that
observations of each species be
compared with relevant literature
to set new data in context and that
observers who are unfamiliar with
the status of birds in a particular
country refer to the ABC country
checklists (www.africanbirdclub.org/
countries/ checklists/index. html) or
more recent or appropriate sources
before submitting records.
Les observations ci-apres sont en
majeure partie non confirmees et
sont publiees uniquement dans le
but d informer. La plupart des
donnees sont de fin 2009 et debut
2010 ; quelques-unes sont plus
anciennes. Nous remercions tous
les ornithologues qui ont pris la
peine de nous faire parvenir leurs
donnees et nous recommandons de
les envoyer, dument documentees,
aux organisations nationales
ou regionales concernees. II est
conseille de verifier le statut des
especes observees dans la litterature
appropriee, afin de mettre les
nouvelles donnees en perspective,
et de consulter notamment les
‘checklists’ des pays africains de
l’ABC (www.africanbirdclub.org/
countries/ checklists/index.html)
ou des sources plus recentes ou
appropriees.
Algeria
Noteworthy species observed during
a short visit on 25-29 October 2009
included several thousand Cory’s
Shearwaters Calonectris diomedea off
Jijel, a Eurasian Griffon Vulture
Gyps fulvus circling around the crags
between Constantine and Jijel, a
Water Rail Rallus aquaticus and
a Eurasian Penduline Tit Remiz
pendidinus at El Kala National Park,
and three Algerian Nuthatches Sitta
ledanti in Tamantut Forest {HB).
Azores
The following records are from
November 2009— May 2010. A pale-
rnorph Trindade Petrel Pterodroma
arminjoniana was photographed
eight nautical miles off Ponta da
Queimada, Pico, on 24 April, whilst
a dark morph was seen between
Pico and Faial on 8 May; the sixth
and seventh records since July 1997
suggest that the species may occur
more frequently in the eastern
Atlantic than previously thought.
A long-staying adult Pied-billed
Grebe Podilymbus podiceps at Lagoa
das Furnas, Sao Miguel, first seen
on 9 November 2008, was still there
with a first-year (since 29 October)
in February; a third was at Lagoa
Azul from 15 November to at least
10 January; one remained on Sao
Miguel into May. At Mosteiros, Sao
Miguel, an adult Brown Booby Sula
leucogaster and up to two Double-
crested Cormorants Phalacrocorax
auritus were present from 8
November until February. A Great
Blue Heron Ardea herodias stayed
at Paul da Praia, Terceira, from
15 February until at least 10 May.
The influx of Blue-winged Teal
Anas discors tapered off with c. 27
still present in early November and
seven at the end of the month. The
fifth Hooded Merganser Lophodytes
cucullatus for the Azores was at
Ponta Delgada, Sao Miguel, from 28
December to at least 29 March.
An adult Purple Gallinule
Porphyrio martinica was on Graciosa
from 9 January until at least 7
February, whilst an American Coot
Fidica americana was on Sao Miguel
from 16 January until at least 26
March. Up to three Semipalmated
Plovers Charadrius semipalmatus
stayed at Cabo da Praia, Terceira,
from 14 January. Up to three
Killdeers C. vociferus at Corvo
airport on 10 January constituted
the 1 1 th record for the Azores; up
to two were there on 24 February,
whilst one was seen on Faial on 26
February. An adult Bonaparte’s Gull
Larus Philadelphia occurred at Praia
da Vitoria, Terceira, on 25 February
and a Glaucous Gull L. hyperboreus
was still at Ponta Delgada, Sao
Miguel, on 9 April. As in previous
years, a Bridled Tern Sterna
anaethetus was present on Ilheu de
Santo Antonio, Pico, in May. On
Flores, Rose-breasted Grosbeaks
Pheucticus ludovicianus were observed
at Ponta Delgada on 22 April (a
male), Fajazinha on 10-19 May (a
female) and Campo Municipal da
Iajes das Flores on 20 May (a male)
(per Birding World 23: 148 &198;
Dutch Birding 32: 52-56, 135-138,
203-214).
Benin
Records from October 2009-June
2010 include the following. A
visit to the ‘W’ National Park on
3-10 February 2010 produced
the following new records for
the W complex {cf Balanqa et al.
2007. Les Oiseaux du Complexe
WAP): Ovambo Sparrowhawk
Accipiter ovampensis (one near Mare
25), White-throated Francolin
Francolinus albogularis (one seen at
close range in the Mekrou Reserve),
African Moustached Warbler
Melocichla mentalis (Mare Boni),
Yellow-breasted Apalis Apalis flavida
Recent Reports
Bull ABC Vol 17 No 2 (2010) - 239
(riparian forest on the Mekrou
River), Pied Flycatcher Ficedula
hypoleuca (regularly encountered
in riparian vegetation), Yellow
Penduline Tit Anthoscopus parvulus
(southern woodland), Western
Violet-backed Sunbird Anthreptes
longuemarei (Mekrou River at
Mekrou), Emin’s Shrike Lanius
gubernator (a female in open wooded
grassland, Mekrou Reserve), Red-
headed Weaver Anaplectes melanotis
(two nests near Keremou), Black-
winged Bishop Euplectes hordeaceus
(flocks near Mare 25 and Point
Triple), Bar-breasted Firefinch
Lagonosticta rufopicta (in riparian
woodland at Chutes de Koudou),
Barka Indigobird Vidua larvaticola
(in breeding dress, near Mare 25)
{FD-L &RJD).
New species for Pendjari National
Park recorded on 10-17 February
2010 include: White-backed Night
Fleron Gorsachius leuconotus (two
on the edge of Mare des Canards
(FD-L, RJDJM&SM), Ovambo
Sparrowhawk (one displaying near
Mare Yangouali), Green Turaco
Tauraco persa (present in evergreen
riparian forest on the Atakora
escarpment at Batia, likely to be the
northern limit of its range) ( FD-L
& RJD), Swallow- tailed Bee-eater
Merops hirundineus (one t.5 km west
of the park entrance at Batia; JM &
SAL), Mottled Swift Fachymarptis
aequatorialis (one drinking in Mare
Sacree is a first record for Benin;
FD-L, RJD, JM & SM), Preuss’s
Cliff Swallow Hirundo preussi (Mare
Bali; FD-L & RJD), Black-backed
Cisticola Cisticola eximius (a pair
in grassland, Circuit Fogou, first
definite record for Benin; FD-L,
RJD, JM & SM) and Togo Paradise
Whydah Vidua togoensis (a male at
Camp des Elephants, moulting out of
dress on 14 February; FD-L & RJD).
Additional new species, observed on
3-5 April are White-fronted Black
Chat Myrmecocichla albijrons (a male
and several females along the track
from Porga to the Batia entrance)
and Bronze-tailed Glossy Starling
Lamprotornis chalcurus (one on
Circuit Fogou) (JM & SM).
Other records from the north
include Melodious Warblers
Hippolais polyglotta at Didani (4
km west of Cobly, Atakora), Cobly
and Touga in late November-early
December, a singing Rufous
Cisticola Cisticola rufus on a treetop
at Didani on 6 June, and an Ortolan
Bunting Emberiza hortidana in
the mountains east of Cobly on 14
November (JM & SM).
Records from the south include
the following. On Nokoue Lake,
a Ramsar Site north of Cotonou,
1 1 heron species were observed in
noteworthy numbers, including c.90
Black Herons Egretta ardesiaca on
17 February (BP). A flock c. 100
African Openbills Anastomus
lamelligerus was seen on 25 October
and c.200 on 14 March ( WP ); groups
usually comprise 30-35 birds (BP).
On 17 February, a Great Snipe
Gallinago media and a Marsh Owl
Asio capensis were flushed at Plaine
du So, Basse Vallee de l’Oueme
(BP). Another Marsh Owl was seen
near the Hotel Germain at Ganvie
on 23 January (AFo, DF, JCB). On
14 and 21 March, three Forbes’s
Plovers Charadrius forbesi were
observed at Plaine du So, with two
Greater Painted-snipes Rostratula
benghalensis also there on 24 April
(WP); an African Crake Crex egregia
was present on 1-14 May (WP,
BP). Collared Pratincoles Glareola
pratincola are common in the area,
with a maximum of c. 100 on 15
November. Black Chlidonias niger
and Whiskered Terns C. hybridus
are also frequent, with maximum of
30 Black on 25 October and at least
ten Whiskered on 24 April (WP).
Flocks of Whiskered Terns were also
observed on Aheme Lake, with 21
birds on 26 February and 35 two
days later; most were moulting into
summer plumage, with one already
in full breeding dress. A flock of up
to 200 first-summer Black Terns was
in Cotonou at the mouth of Nokoue
Lake from 6 May 2009 until at
least mid September. On 24 April,
a group of 6—7 Sooty / Bridled
Terns Sterna Jiiscata / anaethetus was
seen close to the beach at Cotonou
(BP). On 21 March, two Banded
Martins Riparia cincta (possibly
the first for Benin) were seen
amongst a flock of other hirundines
(WP). A Greater Swamp Warbler
Acrocephalus rufescens was heard
and seen well at Plaine du So on 17
February. A presumably ship-assisted
House Crow Corvus splendens was
discovered in Cotonou harbour on 6
February and seen again on 12 May
amongst a group of Pied Crows C.
albus (BP); this appears to be the
first record for Benin of this invasive
species. Groups of Zebra Waxbills
Amandava subflava were seen in
April-May at Plaine du So, with up
to 52 together on 14 May. Slender-
billed Weaver Ploceus pelzelni was
frequent at Ouidah, where birds were
photographed on 4-5 February (AF,
DF, JCB) and at Plaine du So, where
several pairs were regularly seen (BP,
WP).
Botswana
The following records are from
October 2009-June 2010. Black-
necked Grebes Podiceps nigricollis
were at Maun sewage ponds on 19
March (one; RR) and at Sojwe Pan
on 8 May (38; CB). The major influx
of African Openbills Anastomus
lamelligerus into South Africa in
November-January, with some
birds remaining until May, was also
noticed in Botswana (see Bull. ABC
17: 116), with additional sightings
being reported from Masetlheng
Pan on 9—16 December (one; ME),
Bokaa Dam on 13 March (one; CB),
Thagale Dam on 2 May (five; BLB)
and Gaborone Dam on 6 June (one;
IW).
Single Ospreys Pandion haliaetus
were at Gaborone Dam on 3
February (IW) and near Francistown
on 5 March (NBo) and single
European Honey Buzzards Pernis
apivorus at Kasane on 1 9 December
(RP) and Thagale Dam on 23
January (CB). A Pallid Harrier
Circus macrourus was seen at Nata
Sanctuary on 26 March (CV). In
Chobe National Park, 15 Lesser
Kestrels Falco naumanni were
counted on 16 March, 60 the next
day (BE) and 30+ on 18 March (HH
et al.).
Seven Wattled Cranes Bugeranus
carunculatus were in Nata Sanctuary
on 23 December (AF & MM) and
two on 26 March (CV). At Bokaa
240 - Bull ABC Vol 17 No 2 (2010)
Recent Reports
Dam, 180 Black-winged Pratincoles
Glareola nordmanni were observed
on 10 January, with 75 there on
14 March — all had left by 20th;
one was at Thagale Dam on 23
January (CB). A Common Ringed
Plover Charadrius hiaticula was
at Thagale Dam on 2 May (BLB)
and another at Shadishadi Pan on
8 May {CB). Two White-fronted
Plovers C. marginatus were at Maun
sewage ponds on 1 0 March {RR)
and another two at Tshwaane Pan
in 2323D3, outside of the species’
expected range, on 4 April {CB).
Maun sewage ponds attracted
a Pectoral Sandpiper Calidris
melanotos on 6 March {RR) and
Phakalane sewage ponds an African
Skimmer Rynchops flavirostris on 12
October {DD).
A male African Emerald
Cuckoo Chrysococcyx cupreus was
near Maun on 27—29 December
{RR). At Mogobane Dam, 150
Common House Martins Delichon
urbicum were noted on 18 April
{CB). A White-browed Robin Chat
Cossypha heuglini was mist-netted
in Francistown on 24 April, well
outside the species' normal range
{NBo). Warbler records include a
River Warbler Locustella fluviatilis
at Crocodile Pools, Notwane, on
12-20 March {CB), a Blackcap
Sylvia atricapilla at Xakanaxa on 23
December {RP) and two Garden
Warblers S. borin singing from
dense cover in the Kopong Hills on
3 January, with one at Crocodile
Pools on 10 January {CB). Finally,
two Croaking Cisticolas Cisticola
natalensis were observed at Kazuma
Forest Reserve on 14 February {RR).
Burkina Faso
In Arli National Park, just a few
kilometres from the Benin border,
27 African Pygmy Geese Nettapus
auritus were counted on 27
December 2009 (Fig. 1); this species
is considered rare in the park. A
European Roller Coracias garrulus
was also observed there, on 20-21
December; there are few records each
year {JM & SM).
Cameroon
In February 2010, a new species
for the country was discovered at
Douala: Rufous-tailed Palm Thrush
Cichladusa ruficauda {KL, GB &
NV).
A visit in March-April 2010
produced the following records.
A Long-tailed Hawk Urotriorchis
macrourus was seen at Kodmin on 2
April; this seems to be on the edge
of the species’ range. Two juvenile
Steppe Eagles Aquila nipalensis were
identified in Waza National Park
on 19 March; there are very few
documented records for the park
but it seems to be a regular visitor
in small numbers. A Peregrine
Falcon Falco peregrinus of the smaller
resident race minor was displaying
at Mount Kupe on 4 April; there do
not seem to be any previous records
from the mountain but the bird
was behaving as if breeding there.
A male Savile’s Bustard Eupodotis
savilei was flushed in the Waza
area on 20 March; this species is
rarely reported from Cameroon. A
Common Snipe Gallinago gallinago
was seen in Benoue National Park on
22 March and a White-winged Tern
Chlidonias leucopterus on Dang Lake
the next day.
A displaying Green-breasted
Pitta Pitta reichenowi was observed
in Korup National Park on 7
April; this appears to be the first
record for the park of this species,
which has a deeper, flatter voice
than African Pitta P. angolensis.
The continued presence of at least
one pair of Ethiopian Swallows
Hirundo aethiopica around the school
buildings at Nyasoso on 4 April
was noted. A male Rufous-tailed
Rock Thrush Monticola saxatilis
was observed at Poli on 21 April;
this is a very rare Palearctic visitor to
Cameroon. A Great Reed Warbler
Acrocephalus arundinaceus was seen
in Benoue National Park on 22
March. Also there were a Yellow
Penduline Tit Anthoscopus parvulus,
whilst four males and a female Red-
winged Pytilia Pytilia phoenicoptera
were found next day; there are few
records of these species from the
park. Several Chad Firefinches
Lagonosticta umbrinodorsalis were
observed in the Poli area (Fig. 2),
where the species was rediscovered in
2007 (see Bull. ABC 15: 238-241).
At least one pair of Rock Firefinches
Figure I. African Pygmy Geese / Anserelle naine Nettapus auritus, Arli National
Park, Burkina Faso, 27 December 2009 (Johannes & Sharon Merz)
Figure 2. Chad Firefinch /
Amarante de Reichenow Lagonosticta
umbrinodorsalis, Poli area, Cameroon,
21 April 2010 (Nik Borrow)
Recent Reports
Bull ABC Vol 17 No 2 (2010) - 241
L. sanguinodorsalis was seen in the
Maroua area (NB).
Canary Islands
The Purple Swamphen Porphyrio
porphyrio picked up exhausted on
Gran Canaria on 2 October 2009
and ringed and released on 25
October {Bull. ABC 17: 1 17) was
photographed on Lanzarote on
31 December (per Dutch Birding
32: 56). On La Palma, a Long-
billed Dowitcher Limnodromus
scolopaceus stayed near Tazacorte
on 9-16 January {RB). The third
Yellow-browed Warbler Phylloscopus
inornatus for Lanzarote, first seen
23 October, was still present at Uga
on 8 December (per Dutch Birding
32: 59). A Pied Crow Corvus alb us
on Gran Canaria on 22 January
may involve a ship-assisted arrival
present since 2004. The first Black-
and-white Warbler Mniotilta varia
for the Canaries was photographed
at Oasis Park, Fuerteventura, on 18
December (per Dutch Birding 32:
142).
Cape Verde Islands
A male and eight first-winter /
female Ring-necked Ducks Aythya
collaris were at Barragem de Poilao,
Santiago, from 25 February until at
least 5 March (per Birding World 23:
104).
Central African Republic
A Latham’s Forest Francolin
Francolinus lathami was seen near
gallery forest in an area known as
Figure 3. Djibouti Francolin
/ Francolin somali Francolinus
ochropectus , Foret du Day, Djibouti,
February 2010 (Merilyn Browne)
Zamza (08°02’52”N 21°23’38”E),
in the north, on 30 March 2010;
this is well north of the species’
known range as indicated in Borrow
& Demey (2004. Field Guide to the
Birds of Western Africa) ( AP ).
Djibouti
Five Djibouti Francolins Francolinus
ochropectus — a Critically Endangered
Djibouti endemic — were seen on
the escarpment at Foret du Day on
20 February 2010 (Fig. 3). Somali
Starling Onychognathus blythii was
common there. About 60 Arabian
Golden Sparrows Passer euchlorus,
including many males in full
breeding plumage (Fig. 4), were ar
the railway embankment in Djibouti
City on 7th and another 30+ north
of the town on 20th {FIB).
Egypt
In February-May 2010 the following
were reported. A total of seven
Striated Herons Butorides striata
was seen at six sites on 1-15 April.
An adult male Crested Honey
Buzzard Pernis ptilorhyncus flew
north over Hurghada sewage plant
on 4 April. In early April, at least
20 Lappet-faced Vultures Torgos
tracheliotus were counted at Bir
Shalatein. At least four (possibly five)
Three-handed Plovers Charadrius
tricollaris, including a pair with a full-
grown young, were present at the fish
ponds south of Aswan on 1 May. A
Short-eared Owl Asio flammeus was
observed at Wadi Lahami on 7 April.
On 3 March, a Black Scrub Robin
Figure 4. Arabian Golden Sparrow
/ Moineau d’Arabie Passer euchlorus ,
Djibouti City, February 2010
(Merilyn Browne)
Figure 5. Grey Hypocolius /
Hypocolius gris Hypocolius ampelinus,
Nabq National Park, Egypt, 1 1
February (Matteo Gagliardone / Skua
Nature)
Cercotrichas podobe was seen at Wadi
Gimal. The first Pied Crow Corvus
albus for Egypt was photographed
at El Gouna on 1 1 April (per Dutch
Birding 32: 142 & 203-211).
A Grey Hypocolius Hypocolius
ampelinus was digiscoped in Nabq
National Park on 1 1 February (Fig.
5; NS, MG & MB i).
Ethiopia
A Eurasian Bittern Botaurus stellaris
was photographed at Lake Awassa
on 6 January 2010 (Fig. 6); this is
possibly the third confirmed record
for Ethiopia {cf. Ash & Atkins 2009.
Birds of Ethiopia and Eritrea) {DFo).
Five Ferruginous Ducks Aythya
nyroca were on Lake Bishoftu on 1
February and two Pacific Golden
Plovers Pluvialis fulva at Lake
Figure 6. Eurasian Bittern / Butor
etoile Botaurus stellaris , Lake Awassa,
Ethiopia, 6 January 2010 (Dick
Forsman)
242 - Bull ABC Vol 17 No 2 (2010)
Recent Reports
Figure 7. Lesser Crested Tern / Sterne
voyageuse Sterna bengalensis , Lake
Awassa, Ethiopia, 7 January 2010
(Dick Forsman)
Abiata on 1 1th (RSu &FG). Two
immature Lesser Crested Terns
Sterna bengalensis , photographed at
Lake Awassa on 7 and 9 January
(Fig. 7), are apparently the first for
the country — there are no records
for Ethiopia listed in Ash & Atkins
(2009) (DFo).
The Gambia
I hree Cape Gulls Larus dominicanus
vetula were on the beach at Tanji,
Western Division, on 13 January
2010; there have been regular
sightings in recent years. Also in
January, three Adamawa Turtle
Doves Streptopelia hypopyrrha were
seen at Janjangbureh, Central River
Division (NB).
Ghana
In February 2010, a Spot-breasted
Ibis Bostrycbia rara was seen and
heard flying over the canopy walkway
in Kakum National Park at dusk on
25th. An American Golden Plover
Pluvialis dominica was photographed
at Cape Coast Lagoon on 26th
(Fig. 8) and a Pectoral Sandpiper
Calidris melanotos at Sakumono
Lagoon two days later, at almost
exactly the same spot where one was
found a year previously (CT).
Records from April-May 2010
include the following. A Spot-
breasted Ibis was flushed from the
forest floor in Ankasa in early May.
A juvenile Ayres’s Hawk Eagle
Hieraaetus ayresii was seen in Kakum
National Park on 4 May; there
Figure 8. American Golden Plover /
Pluvier bronze Pluvialis dominica , Cape
Coast Lagoon, Ghana, 26 February
2010 (Chris Townend)
appear to be few documented records
lor the park. At Ankasa, a Sandy
Scops Owl Otus icterorhynchus was
heard at dusk on 26 April. Six Black
Spinetails Felacanthura melanopygia
flying over the White-necked
Picathartes Picathartes gymnocephalus
site at Bonkro had been presumably
forced down by the impending
storm. A Yellow-footed Honeyguide
Melignomon eisentrauti was observed
at Atewa, whilst an African Piculet
Sasia africana was found in Bobiri
Forest in May.
A pair ol Nimba Flycatchers
Melaenornis annamarulae was
observed high up in a large tree at
Atewa in May; this Upper Guinea
forest endemic has only recently
been discovered in Ghana (see
Bull. ABC 15: 95-96). Tessmann’s
Flycatchers Muscicapa tessmanni
were seen in Kakum National Park
(one singing) and at Aboabo (a pair
feeding two recently fledged young);
a photograph of these birds appears
to be the first of the juveniles of
this little-known species (Fig. 9). A
Lagden’s Bushshrike Malaconotus
lagdeni in Bobiri Forest on 29 April
(Fig. 10) was making a previously
undescribed call almost identical to
that of Fiery-breasted Bushshrike M.
cruentus ; the first-named species is
very rare in Ghana. In May, Red-
fronted Antpeckers Parmoptila
rubrifrons were observed at Abrafo (a
pair), Ankasa (a pair) and Aboabo (a
family group) (NB).
Figure 9. Tessmann’s Flycatcher
Muscicapa tessmanni with young,
Aboabo, Ghana, 28 April 2010 (Nik
Borrow)
Gobemouche de Tessmann Muscicapa
tessmanni avec jeunes, Aboabo, Ghana,
28 avril 2010 (Nik Borrow)
Figure 10. Lagden’s Bushshrike /
Gladiateur de Lagden Malaconotus
lagdeni , Bobiri Forest, Ghana, 29 April
2010 (Nik Borrow)
Guinea
In January-February 2010, a search
lor Nimba Flycatcher Melaenornis
annamarulae in south-eastern Guinea
found a total of 15 pairs at four of
the seven surveyed sites. The species
was encountered at Douama, sous-
prefecture de Binikala (four pairs),
sous-prefecture Sengbedou-Macenta
(three pairs), Tetini Forest Reserve
(four pairs) and Mount Bero Forest
Reserve (four pairs). It was not found
in Diecke Forest Reserve, nor in
the sous-prefecture de Bounouma
or at Mount Yonon. In Guinea, the
species was previously known only
from Ziama, Dere and Pic de Fon
(MBC&KS).
Recent Reports
Bull ABC Vol 17 No 2 (2010) - 243
Kenya
The following reports are from
January-June 2010, with additional
records from October-December
2009 not mentioned in previous
Recent Reports. A Madagascar
Pond Heron Ardeola idae at Sabaki
on 1 1 February is an unusual record
for the season. More than 5,000
White Storks Ciconia ciconia were
at Nakuru National Park (=NP)
on 20-21 February. A total of 94
Eurasian Honey Buzzards Pernis
apivorus on Mount Elgon on 7
March is an unusually high count. A
first-year Egyptian Vulture Neophron
percnopterus was on the Magadi
road, c. 20 km before the lake, in late
January; all records of this species are
worth reporting given its significant
decline. An immature Black-chested
Snake Eagle Circaetus pectoralis
near Kapcherop, Cherangani, on
24 December, and an Eastern
Chanting Goshawk Melierax
poliopterus in Nairobi NP on 27
December are unusual records for
those areas. A flock of 23 Levant’s
Sparrowhawks Accipiter brevipes
was at the Ahero rice scheme on
24 January and an adult male near
Mtito Andei on 30 January; this is
an unprecedented number of this
Accipiter for which there are only
c.G previous records in Kenya. A
Long-legged Buzzard Buteo rufinus
at Nakuru NP in January was still
present on 21 February. Unusual
records for February include a female
Amur Falcon Falco amurensis at
Solio Ranch, Laikipia, on 18th and
an Eleonora’s Falcon F. eleonorae
at Tsavo East NP on 13th. A Grey
Kestrel F. ardosiaceus at Nakuru NP
on 28 February is a rather easterly
record.
A Red-chested Flufftail
Sarothrura rufa was reported from
Kiboko Bay, Lake Victoria, on 3
May. A Corncrake Crex crex was
ringed at the Botanic Gardens,
National Museums of Kenya,
Nairobi; this is a rare bird away
from the Mara and very few have
been ringed in Kenya. A Buff-
crested Bustard Eupodotis gindiana
was unusually close to the sea near
the salt pans at Kurawa, north of
Malindi, on 24 April. Four Eurasian
Oystercatchers Himantopus ostralegus
stayed at Mida Creek, Watamu,
through much of February-April.
Unprecedented numbers of Caspian
Plovers Charadrius asiaticus were
recorded: c.70 west of Siana Springs
in late January and 2,347 together
on the Tana River Delta on 15
February; very few were seen in the
usual wintering grounds of the Masai
Mara. In March, a Temminck’s
Stint Calidris temminckii was seen
and a Red-necked Phalarope
Phalaropus lobatus ringed at Lake
Nakuru. Over 1,500 Brown
Noddies Anous stolidus were around
Whale Island, Watamu, on 16 May;
although likely to breed at the site,
there is no evidence yet. A huge tern
roost, discovered a few years ago at
Sabaki River mouth, contained an
estimated 500,000 birds in February.
Two Common Black-headed Gulls
Larus ridibundus were on a dam near
Molo on 2 May; there are few reports
away from the Rift Valley lakes.
A Yellowbill Ceuthmochares
aereus was seen at Langata, Nairobi,
on 19 November — this is a rare
species around Nairobi. Single
Black Coucals Centropus grillii were
reported from Aruba Dam, Tsavo
East NP, on 13 February and near
Witu Forest, Tana River Delta,
on 26 April. A Bohm’s Spinetail
Neafrapus boehmi at Witu Forest,
Tana River Delta, on 26 April is
an interesting record, as Arabuko-
Sokoke is generally considered to
be its northernmost limit. Several
thousand Common Swifts Apus
apus were at Sagala, Voi, on 23
January — such large numbers
are unexpected at this season. A
White-headed Mousebird Colius
leucocephalus at Sagala, Voi, on 24
January was outside its normal range.
Eight White-throated Bee-eaters
Merops albicollis at Naibor Camp,
Masai Mara, on 8 June is an unusual
date, whilst >100 Blue-cheeked
Bee-eaters M. persicus near Witu,
Tana River Delta, on 26 April is
a late date. About 20 Madagascar
Bee-eaters M. superciliosus were at
Sagala, Voi, on 23 January. At least
1 ,000 European Rollers Coracias
garrulus near Voi on 24 January
were still present on 13 February.
An Usambiro Barbet Trachyphonus
darnaudii usambiro west of the
Ngong Hills, Rift Valley, on 14
March is the easternmost report for
this taxon so far, whilst one in well-
watched Nairobi NP on 31 March
was new for the park. A Tullberg’s
Woodpecker Campethera tullbergi
in Kakamega Forest on 7 May is an
unusual record for this site.
An immature Red-winged Lark
Mirafra hypermetra on a grassy area
bordering the beach at Watamu
on 23 May was definitely out of
place: larks are very rare on the
coast, let alone on the beach front.
A pair of Rufous-chested Swallows
Cecropis semirufa was nesting in a
warthog hole in the Masai Mara,
in March; there are relatively few
breeding records for this species.
In late January, two Bush Pipits
Anthus caffer were observed at Siana
Springs. Three Little Greenbuls
Andropadus virens south of Kilifi
on 1 February are the first records
north of Mombasa for many years.
Records from Nairobi NP include a
small flock of Grey-olive Greenbuls
Phyllastrephus cerviniventris on 25
November (only the third record
for the park), a Bare-eyed Thrush
Turdus tephronotus on 27 March
(first record for Nairobi district) and
a Basra Reed Warbler Acrocephalus
griseldis on 29 November (second
record for the park). Barred
Warblers Sylvia nisoria were reported
as extremely abundant — ‘the most
abundant migrant after European
Rollers, outnumbering Common
Whitethroats S. communis 1 5 to
T — at Sagala, Voi, on 24 January.
An Olive-tree Warbler Hippolais
olivetorum at Tsavo East NP on 13
February was probably overwintering,
which is very unusual in Kenya;
one in Nairobi on 13 March is an
unusual record for this site. DNA
analysis of an unusual Acrocephalus
ringed at Ngulia, Tsavo West NP,
in December, proved the bird was a
hybrid Marsh A. palustris x Blyth’s
Reed Warbler A. dumetorum. A
pair of Yellow-vented Eremomelas
Eremomela icteropygialis just outside
Sala Gate, Tsavo East NP, on 12
February, is a very southerly record.
244 -Bull ABC Voi 17 No 2 (2010)
Recent Reports
A group of Hinde’s Babblers
Turdoides hindei was discovered
in a valley 34 km south-east of
Machakos on 23 January; this is a
new site for this Kenyan endemic.
Boubous photographed and tape-
recorded on Manda Island, Lamu,
in April appear to be black-morph
Erlanger’s Boubous Laniarius
erlangeri ; if accepted it will be a new
species for Kenya (for a video grab
see http://naturekenyalOOO.ning.
com) — hitherto it was considered
to be a southern Somalia endemic.
Three House Crows Corvus splendens
at Maungu, Voi, are among the
furthest inland records of this
invasive species and an indication
ol its massive increase since the
control programme ceased in late
2004. A Fischer’s Starling Spreo
fischeri at Ol Kejo bridge, Magadi
Road near Olorgesailie, on 31
March is one of the few (the first?)
records for the Rift Valley. Groups
of Magpie Starlings Speculipastor
bicolor were present at Sagala, Voi,
on 23 January — this species is
recorded this far south only every
few years; two on Mpala Ranch
on 10 February is a very westerly
record. A pair ol Sharpe’s Starlings
Cinnyricinclus sharpii was feeding
nestlings in South Marmarnet Forest,
Nyahururu, on 1 1 March. An adult
male Red-headed Weaver Anaplectes
rubriceps at the entrance of Nairobi
NP on 27 December was only the
second record for the park. A small
Rufous-tailed Weaver Histurgops
ruficaudus colony of seven nests with
begging young and one recently
fledged juvenile were found at the
Mara River, Masai Mara, on 14
April; this species was only recently
added to the Kenya list and this
is the first reported breeding. In
March, the second record of Straw-
tailed Whydah Vidua fischeri in
Nairobi NP was made when a male
was observed. A briefly seen Somali
Golden-breasted Bunting Emberiza
poliopleura on the western outskirts
of Nairobi on 17 October is a new
species for the city [C]).
Libya
Two nests of Little Bitterns
Ixobrychus minutus , one with four
eggs and the other with egg shell
fragments, were found near Lake
Bu Tesira, Benghazi, on 30 April
and 1 May 2010; this is a new
breeding species for Libya. Collared
Pratincole Glareola pratincola was
also discovered to be a local breeder:
at least eight pairs and a nest with
one egg were found at A1 Marj,
Cyrenaica, on 10 May. Zitting
Cisticola Cisticola juncidis was found
to be a common breeder at Taurgha,
Tripolitania, on 27-28 April. A flock
of 15 Tree Sparrows Passer montanus
was observed at A1 Khums on 26
April and up to 12 Red Avadavats
Amandava amandava near Lake Bu
Tesira on 30 April-6 May; these
species probably also breed in the
country (JH & EF; per Birding World
23: 198).
Madeira
Noteworthy records from February-
May 2010 include the following. A
peculiar Zino’s Petrel Pterodroma
madeira with largely white wings
and very pale upperparts and head
(possibly a morph of another species)
was observed for the third time in
Madeiran waters on 1 3 May and
filmed (see www.madeirawindbirds.
com). On 8 May, a Black-capped
Petrel P. hasitata was reported
twice from a cruise ship north-east
of Madeira. A Ring-necked Duck
Aythya collaris was at Porto Santo on
28 February and a Purple Sandpiper
Calidris maritima at Canigal
harbour on 30 April. A Hudsonian
Whimbrel Numenius phaeopus
hudsonicus was present at Sao Vicente
on 22 February. The second Red
Phalarope Phalaropus fulicarius for
the archipelago was seen north of
Madeira on 15 May (per Birding
World 23: 60, 104 & 198; Dutch
Birding 32: 138 & 203).
Morocco
Records from November 2009-May
2010 are as follows. At Tetouan,
the first Leach’s Storm-petrel
Oceanodroma leucorhoa for the
country’s Mediterranean coast was
found exhausted on 9 January (per
Birding World 23: 13). A male Lesser
Scaup Aythya affiwis was discovered
at Oued Massa on 1 1 February ( MB
& DPI). At least one White-headed
Duck Oxyura leucocephala remained
at Sidi Bou Rhaba, Kenitra, during
April. At Merzouga, Tafilalt, 1-2
Eurasian Bitterns Botaurus stellaris
were singing at Dayet Srij on 9 April;
this is the south-easternmost record
for Morocco, where the species is
less than annual in coastal marshes
in the north. The long-staying
Western Reef Egret Egretta gularis
at Essaouira, first found on 19
April 2009, was still present on 27
February. An adult Lesser Flamingo
Phoeniconaias minor was foraging
among a flock of c.100 Greater
Flamingos Phoenicopterus [ruber)
roseus north of Oualidia, 68 km
south of El Jadida, on 1-5 May (per
Dutch Birding 32: 135 &1 99-203).
A Tawny Eagle Aquila rapax was
seen at Merzouga on 6 February [MB
&DH).
Several Baillon’s Crakes Porzana
pusilla were found in flooded fields
at Oued Massa in the second week
of April; there are only two previous
records for Morocco in the past 15
years. At Khnifiss lagoon, Tarfaya,
in the south-west, up to nine Cape
Gulls Larus dominicanus vetula
stayed from 1 8 November to at
least April; at least eight with one
active nest were counted on 14-29
April. At Oued Souss, Agadir, c.450
km further north, an adult was
photographed on 12 April and two
Laughing Gulls L. atricilla were
there on 19 April. A Grey-hooded
Gull Larus cirrocephalus was noted
at Dakhla, Western Sahara, on a few
dates between January and April.
In the south-east, the first Dunn’s
Larks Eremalauda dunni for the
Tafilalt were observed from 1 1
April near Merzouga; on 3 May,
eight birds and a nest were found at
three sites (the first records for the
country were from Oued Ad-Deheb,
Western Sahara, in 2006). A
Dupont’s Lark Chersophilus duponti
was singing at Tizi-n-Taghatine,
west of Tazenakht, on 7 and 11
April. Eastern Olivaceous Warblers
Hippolais pallida of the North
African race reiseri were found again
in increasing numbers in suitable
habitat in the south. A total of 25
Cricket Warblers Spiloptila clamans
Recent Reports
Bull ABC Voi 17 No 2 (2010) -245
was counted west of Aousserd,
Western Sahara, on 12 December;
55 were found on 24 January, and
a male was seen feeding nestlings
on 13 February. A Woodchat
Shrike Lanius senator of the race
badius , the fourth for Morocco,
was photographed 41 km west
of El Kelaa on 27 March. Three
Pied Crows Corvns albus c. 160 km
north-east of Dakhla, first seen on
13 December, were breeding on a
pylon on 25 April; these constitute
the first for Morocco. It appears that
2—3 birds have been present here for
three years, but there are no previous
proven breeding records (per Dutch
Birding 32: 56-65, 138 & 205-211).
Mozambique
A White-tailed Tropicbird
Phaethon lepturus was reported c.26
nautical miles off Ponto d’Oura in
early May 2010. On 15 March at
Catapu, a worm-infested Cordyla
tree in the forest held no fewer
than nine cuckoo species including
a Madagascar Cuckoo Cuculus
rochii and two Lesser Cuckoos C.
poliocephalus (per TH).
Namibia
Records from January-June 2010
include the following. An African
Openbill Anastomus lamelligerus
stayed at Windhoek from 8 March to
at least 1 1 April. Also at Windhoek,
an Osprey Pandion haliaetus was at
Avis Dam on 9 May. A Bat Hawk
Machieramphus alcinus reported
from Kakuse Farm, c.70 km north-
west of Tsumeb, in early April was
notable. A young Palm-nut Vulture
Gypohierax angolensis was found
dead at Walvis Bay on 22 June.
Three Three-handed Coursers
Rhinoptilus cinctus, including a chick,
were ringed on Kakuse Farm on 1 5
May; there are very few records from
north-central Namibia and, although
the species is sporadically reported
from the Caprivi, the nearest
reasonably sized population probably
is in western Zimbabwe. Two
Common Redshanks Tringa totanus
remained at Mile 4 Salt Works near
Swakopmund throughout the period
and apparently were going to spend
the southern winter there; one was
also observed at Walvis Bay on 28
February. Red-necked Phalaropes
Phalaropus lobatus were seen in
Walvis Bay from February to May,
with at least three individuals on 28
February and up to 13 on 9 May. A
Red Phalarope P. fidicarius was at
Mile 4 Salt Works near Swakopmund
on 8 April. A Franklin’s Gull Lams
pipixcan and a Common Black-
headed Gull L. ridibundus were still
present at Walvis Bay at the end of
February (per TH).
Niger
The highlight of early 2010 was
the presence of ‘Dorottya’, a
satellite-tracked Saker Falcon Falco
cherrug, which mostly remained
r.50 km north ofZinder (http://
www.sakerlife.mme.hu/en/gmap).
The falcon was seen twice during
a research project into its ecology
in February {HI). The sighting of
another Saker Falcon in Nguigmi, on
13 November 2009 {SW), has been
accepted. Arguably as stunning was
the appearance of photographs of an
adult Greater Kestrel F. rupicoloides,
probably of the subspecies fieldi,
taken at Termit, in the south-east,
during a Sahara Conservation Fund
expedition in February 2009 ( 77?
per TW). The nearest known records
of this species are from Sudan on
the border with Ethiopia, 2,500 km
away.
Additional reports from December
2009-June 2010 include the
following. Quite far north are records
of breeding Bateleur Theratopius
ecaudatus (fledgling at nest with
adults) and of a single Savile’s
Bustard Lophotis savilei, both at
Gadabeji in March {TW). A Spotted
Sandgrouse Pterocles senegallus with
three young was seen at Gadafaoua,
south-east of Agadez, in June {TW).
Also noteworthy is the finding of
a nest with two eggs of Golden
Nightjar Caprimulgus eximius , on 1
June at Taguedoufat, 100 km south-
east of Agadez (Figs. 1 1—13; TW).
The recently opened Niger Bird
DataBase website, www.bromus.net/
nibdab/, is already paying dividends.
Singing Dunn’s Larks Eremalauda
dunni were reported east of Termit
on 15 December {TW). Eurasian
Golden Orioles Oriolus oriolus
passed through Maine-Soroa during
the second half of April and Masked
Shrikes Lanius nubicus were quite
frequent there in February {DK).
House Sparrows Passer domesticus
appear to be well established and
spreading in south-east Niger. The
country’s first record was from Djado
in the far north-east in 1970; the
second concerned a single male in
Nguigmi, north-east of Lake Chad,
on 21 August 2003. Although a
search for this species at the latter
site in 2005 was unsuccessful {cf.
Malimbus 30: 47), a single was
seen there on 22 April 2006 {AM).
Figures 11-13. Golden Nightjar Caprimulgus eximius with eggs, Taguedoufat, Niger, early June 2010 (Tim Wacher)
Engoulevant dore Caprimulgus eximius et ses oeufs, Taguedoufat, Niger, debut juin 2010 (Tim Wacher)
246 - Bull ABC Vol 17 No 2 (2010)
Recent Reports
Four years later, on 20 April 2010,
‘lots’ were coining every day to a
waterbowl in the same town (SWJ,
and a pair was reported from a petrol
station in Maine-Soroa, 100 km west
of Lake Chad, on the border with
Nigeria, in February (DK) (all per
JB).
Rwanda
A pair of Green-backed Eremomelas
Eremomela canescens found in open
woodland in Akagera National Park
on 8 April 2010 appears to be the
first lor Rwanda. The grey crown
and nape, blackish mask, contrasting
green upperparts, white throat and
upper breast, and yellow lower breast
and belly were clearly seen (JA ).
Senegal
Records from January-March 2010
include the following. A Eurasian
Bittern Botaurus stellaris was
observed in Djoudj National Park
on 21 January; there are very few
records for the park. Sightings of
pale Grey Herons Ardea cinerea at
Langue de Barbarie on 18 January
and in the Djoudj on 20th were
probably of the race monicae, which
has been recorded as a vagrant from
Mauritania. An Allen’s Gallinule
Porphyrio alleni and two Short-eared
Owls As io flammeus were seen in
the Djoudj, on 22 January (NB).
Also there, a Common Crane Grus
grus was photographed with Black-
crowned Cranes Balearica pavonina
on 22 and 25 March; this appears to
be the first country record (per Dutch
Birding 32: 205). A flock of c.8
Fulvous Babblers Turdoides fulvus
was seen near Richard-Toll (NB).
In April, at least two Narina’s
Trogons Apaloderma narina were
photographed on several dates in
semi-decidious and gallery forest at
Dindefelo, in the extreme south-east,
near the border with Guinea-
Conakry; this is a new species for the
country — full details will appear in
the next Bull. ABC ( NA , LP & IZ).
Seychelles
The following records are mainly
from the period October 2009— May
2010, with a few from earlier
dates. Never have so many reports
ol rarities been received since the
Seychelles Bird Records Committee
(SBRC) was formed in 1992.
Accepted firsts are Bulwer’s Petrel
Bulweria fallax (one at Cousin Island
on 15 June 2009), Alpine Swift
Tachymarptis melba (one on Bird
Island on 20—21 November), Desert
Wheatear Oenanthe deserti (a first-
winter male on Bird Island on 16-19
November) and Common Stonechat
Saxicola torquatus (one on Denis on
27 December). This takes the total
number of species on the Seychelles
list to 254. First reports of Herald
Petrel Pterodroma heraldica on
Cousin on 10-11 June 2009 and of
European Pied Flycatcher Ficedula
hypoleuca on Bird Island are currently
being examined.
Second reports for Seychelles,
all from Bird Island, include a
first-winter female Pied Wheatear
Oenanthe pleschanka on 1 3-20
November and a male Blackcap
Sylvia atricapilla on 16 November.
A record of a snipe on 12 November
was accepted as either Pintail Snipe
Gallinago stenura or Swinhoe’s
Snipe G. megala ; this is the second
such record, whilst there is only
one confirmed record of Pintail
Snipe. A first-winter bunting on 21
November was accepted as either
Ortolan Bunting Emberiza hortulana
or Cretzchmar’s Bunting E. caesia ;
there is only one accepted record of
Ortolan and none of Cretzchmar’s.
Third reports include a Reed
Cormorant Phalacrocorax africanus
on Grand Terre, Aldabra, on 16
February, a Stone-curlew Burhinus
oedicnemus on Alphonse on 7—9
December, a Great Knot Calidris
tenuirostris on Desroches on 3-5
March, and an Icterine Warbler
Elippolais icterina on Bird Island
on 12 November. Single Wood
Warblers Phylloscopus sibilatrix on
Bird Island on 17 and 27 November
were the third and fourth records.
Fourth records were a Squacco
Heron Ardeola ralloides on Praslin
on 12 January, a Greater Short-toed
Lark Calandrella brachydactyla on
Bird Island on 16-23 November,
with two present on the final date,
and a female / immature Rufous-
tailed Rock Thrush Monticola
saxatilis on Bird Island on 14
November.
The sixth Wilson’s Storm-
petrel Oceanites oceanicus for
the archipelago was observed off
D’Arros on 3 July 2009. A belated
report of an Indian Pond Heron
Ardeola gray ii on Denis on 10
December 2007 was the fifth for
Seychelles; singles were also recorded
on Alphonse on 30 October-5
November, and on Desroches. A
Glossy Ibis Plegadis falcinellus on
Fregate on 8-1 1 November and
another on Bird Island on 10-17
November constituted the fifth
and sixth records. A Lesser Kestrel
Falco naumanni was on Desroches
on 8 March (sixth record). Single
Common Pratincoles Glareola
pratincola were on North Island on
25 September (earliest post-breeding
arrival date), Alphonse on 5-14
November and Bird Island on 1 1
November (nine previous records).
Reports ol Black-winged Pratincole
G. nordmanni included four adults
on Alphonse on 4-16 May 2009,
one on Fregate on 12 June 2009, one
on Bird Island on 1 1-28 November,
two on Fregate on 14 November and
one on Desroches on 1 March; there
are six previously accepted records.
A Pectoral Sandpiper Calidris
melanotos was on Alphonse on 8-16
May (fifth record). A belated report
of a Whiskered Tern Chlidonias
hybridus at Victoria, Mahe, on 1 1
October 2006 was the fifth for
Seychelles. Two Little Swifts Apus
ajfinis were seen on Cousine on 20
January (fifth record). A Common
House Martin Delichon urbicum
on Alphonse on 4-5 October and a
Grey Wagtail Motacilla cinerea on
North Island on 18-19 November
were the ninth records for both
species.
A ring found at the Alphonse
airstrip on 12 December 2009
had been applied to a first-year
Eleonora’s Falcon Falco eleonorae
at Las Islas Columbretes, Spain, on
17 September 2008. It is assumed
that the bird died on Alphonse and
the ring became detached; there
have been 28 previous records of
this species. Eurasian Hobbies F.
subbuteo were reported from D’Arros
Recent Reports
Bull ABC Vol 17 No 2 (2010) -247
on 21 November, Bird Island on
15- 21 November (two), F regate on
17 November, Poivre on 7 December
and Desroches on 3-4 January;
all were immatures (21 previous
records). Common Cuckoos Cuculus
canorus were observed on Alphonse
on 15-22 January 2009, Desroches
on 23 October-26 November, Roche
Caiman, Mahe, on 18 November,
North Island on 16 November- 1
December, Bird Island on 16-26
November (with two present on
19-20 November), Cousine on 4
December and 25 December-2
January, Praslin on 12 January and
Aride on 14 January (26 previous
records). Lesser Cuckoos C.
poliocephalus were present on Bird
Island on 22 November, at Anse
aux Pins, Mahe, on 13 January-27
February, with two there on the
final date, and on Cousine on 10-13
January and 21 January-20 February
(13 previous records).
For the third time in living
memory and for the second
consecutive season, there were reports
of Blue-cheeked Bee-eaters Merops
persicus in significant numbers,
including 20-25 on Bird Island
on 8-25 November, one at Roche
Caiman Bird Sanctuary, Mahe, on
18 November, six on North Island
on 18-19 November, two on Cousin
on 19 November, six on Conception
on 23 November, two on Aride on
16- 20 November, one on Alphonse
on 28 November, at least one on
Denis on 2-12 December, four on
D’Arros on 1 5 December, and one
on Silhouette on 15—16 December.
Apart from the three years when
invasions took place, there have been
17 accepted records.
Further records of interest include
a Little Egret Egretta garzetta on
Cousine on 5 February-3 March
(26th record), a Great Egret E.
alba at Beau Vallon marsh, Mahe,
on 14 November and another on
Bird Island on 9-11 November (14
previous records), an adult Purple
Heron Ardea purpurea at Roche
Caiman Bird Sanctuary, Mahe,
from about 18 October to at least
18 November, with an immature
on Alphonse on 22 October, one
on Desroches on 24 October- 17
November and another immature
on Bird Island on 1 1-21 November
(37 previous records), a female or
immature Northern Shoveler Anas
clypeata on Aride on 5 January (tenth
record), an immature Northern
Pintail A. acuta on Aride on 20
January (1 1th record), a Ruff
Philomachus pugnax on Desroches
on 16 November, with two on
Bird Island on 13-28 November
(28 previous records), a Common
Snipe Gallinago gallinago on Aride
on 17 October, two on Alphonse
on 20 October-6 November and
two on Denis on 30 December (14
previous records), a Black-tailed
Godwit Limosa limosa on Aride
on 24 December (seventh record),
a Common Black-headed Gull
Larus ridibundus on Cousine on
20 January (17th record), an adult
Gull-billed Tern Sterna nilotica off
Bird Island on 18 November (11th
record), a Common Swift Apus
apus on Desroches on 5 February
(19th record), a Pacific Swift A.
pacificus on Bird Island on 1 1—15
November, with another on Denis
on 26-27 December (12th- 13th
records), a European Roller
Coracias garrulus on Bird Island on
10-27 November and 18 March,
with others on Fregate on 1 1—13
November, Praslin on 16 November,
Desroches on 17-25 November
and 7-17 February, Alphonse on
25-28 November (two) and 14
March, and Denis on 2 December
(34 previous records), an adult
Broad-billed Roller Eurystomus
glaucurus on Alphonse on 10-22
November ( 1 4th record east of the
Aldabra group), a Common Sand
Martin Riparia riparia on Alphonse
on 20-26 October, with another
on Bird Island on 9—1 1 November
(18 previous records), a White
Wagtail Motacilla alba on D’Arros
on 7 November, with others on
Desroches on 26 November and on
Bird Island on 15-20 November
(27 previous records), a first-winter
Yellow Wagtail M. flava on Aride
on 20-25 November (31st record),
an adult and up to four first-winter
Red-throated Pipits Anthus cervinus
on Bird Island on 1 1-25 November
(17th record), a Common Redstart
Phoenicurus phoenicurus on Bird
Island on 1 1 November (1 1th
record), a Northern Wheatear
Oenanthe oenanthe on Denis on 3
January and another on Aldabra on
14 January (45 previous records),
and a female / immature Eurasian
Golden Oriole Oriolus oriolus on
Bird Island on 1 1 November, with
another on Cousine on 24 December
(14 previous records) (AS).
Sierra Leone
During a visit in February 2010
the following records were made.
A flock of 40 African Openbills
Anastomus lamelligerus was found
at Bumbuna on 17th; there appear
to be no previous records from this
area. The same day, a Beaudouin’s
Snake Eagle Circaetus beaudouini
was near a bush fire north of Mile
91; this is slightly south of the range
given in Borrow & Demey (2004.
Field Guide to the Birds of Western
Africa). Cassin’s Hawk Eagles
Spizaetus africanus were observed at
Guma Dam on 6th and at Tacugama
on 19th; although the species has
been noted there in recent years,
there are apparently no historical
records from the peninsula. A Great
Snipe Gallinago media was noted in
a swamp in Gola East and another
in the rice fields at Kenema. Two
Brown Nightjars Veles binotatus
were seen at Tiwai on 10th; this
species was only recently discovered
here. Three Red-throated Pipits
Anthus cervinus were at the Kenema
rice fields on 1 2th, where it seems
to be regular (Borrow & Demey
2001 show only one previous record
for the country). A pair of Gola
Malimbes Malimbus ballmanni with
two full-grown young were seen in
Gola North ( NB ).
Somalia
The following were reported from a
pionering bird tour to Somaliland in
February 2010. An adult Archer’s
Buzzard Buteo augur archeri was
seen on the Daallo Escarpment
on 15th. Two chestnut-winged
francolins flushed at the same site
appeared to fit the description of
Archer’s (Orange River) Francolin
Francolinus levaillantoides lord,
248 -Bull ABC Vol 17 No 2 (2010)
Recent Reports
Figure 14. Heuglin’s Bustard /
Outarde de Heuglin Neotis heuglinii ,
male, Inaafmadobe, Somalia,
February 2010 (Merilyn Browne)
Figure 15. Little Brown Bustard
/ Outarde somalienne Eupodotis
humilis , male, Inaafmadobe, Somalia,
February 2010 (Merilyn Browne)
Figure 16. Somali Short-toed Lark /
Alouette roussatre CaLindrella somalica
percofusa, Wajaale Plains, Somalia,
February 2010 (Merilyn Browne)
Figure 17. Lesser Hoopoe Lark /
Sirli de Witherby Alaemon hamertoni,
Banabe Plains, Somalia, February
2010 (Merilyn Browne)
Figure 18. Gillett’s Lark / Alouette
de Gillett Mirafra gilletti arorihensis ,
Qorlilugud, Somalia, February 2010
(Merilyn Browne)
Figure 19. Somali Wheatear /
Traquet de Somalie Oenantbe
phillipsi, Hargeisa, Somalia, February
2010 (Merilyn Browne)
although it cannot be excluded that
they were Yellow-necked Spurfowl
F. leucoscepus, which was observed
nearby. Three Red-knobbed
Coots Fulica cristata were found
at Waajale Twon reservoir on 9th;
this species is not mentioned for
the north of Somalia in Ash &
Miskell (1998. Birds of Somalia) .
Two males and a female Heuglin’s
Bustard Neotis heuglinii were seen
near Inaafmadobe, Qorlilugud, and
on the Banade Plains, respectively,
on 1 3th— 1 5th (Fig. 14). Little
Brown Bustards Eupodotis humilis
were common in suitable habitat
throughout; they were encountered
daily, with a maximum of five on
15th (Fig. 15).
Three very tame Somali Larks
Mirafra somalica were photographed
on the Banade Plains on 15th (Fig.
16). Also there were three Foxy
Larks M. alopex of the nominate
race alopex, whilst the large, rather
pipit-like Lesser Hoopoe Lark
Alaemon hamertoni was numerous,
with up to 15 sighted on 1 4th, with
one performing its characteristic
song flight (Fig. 17). Two Gillett’s
Larks Mirafra gilletti of the pale
race arorihensis were watched
near Qorilugud on 1 4th (Fig.
18). Blanford’s Lark Calandrella
blanfordi of the distinctive race
daroodensis was seen on the Waajale
Plains on 9th and on the Banade
Plains on 1 4th; at both localities
Somali Short-toed Lark C. somalica
was common.
Somali Thrush Turdus ( olivaceus )
ludoviciae was observed at Ga’an
Libah on 1 1 th— 12th (several) and
was the commonest bird on the
upper Daallo Escarpment with up
to 20 seen per day (Fig- 20); this
Figure 20. Somali Thrush / Merle de
Somalie Turdus ( olivaceus ) ludoviciae,
Daallo, Somalia, February 2010
(Hugh Buck)
Recent Reports
Bull ABC Vol 17 No 2 (2010) -249
endemic blackbird is often lumped
with the widespread but dissimilar
(both in appearance and habitat
choice) Olive Thrush T. olivaceus of
East Africa. It is now increasingly
recognised as a Somali endemic
restricted to the few patches of
highland juniper forest in the north
of Somaliland. Somali Wheatear
Oenantbe phillipsi was common in
all rocky habitats (Fig. 19), whilst
Philippa’s Crombec Sylvietta
philippae appeared to be frequent in
Acacia bush north of Inaafmadobe
and near Qorilugud, with up to
ten seen. Six Pale Rockfinches
Carpospiza brachydactyla at a watering
hole near Wajaale town on 9th was
an unexpected find; this species has
previously been recorded in Djibouti,
Eritrea and Ethiopia but apparently
not in Somalia. A young male
Somali Golden-winged Grosbeak
Rhynchostruthus louisae was observed
on the Maydh road on 16th. A single
Warsangli Linnet Carduelis johannis
was seen along the Daallo— Maydh
road at c. 1,800 m; this species is
endemic to the mountains of north
Somaliland and Daallo is in the far
west of its range ( HB ).
South Africa
Records from December 2009-June
2010 include the following. A Grey-
backed Storm-petrel Garrodia nereis
observed 16 nautical miles south-west
of Cape Point on 27 December was
only the second record for southern
Africa and the African continent.
Other noteworthy records made
at sea south-west of Cape Town
include a Wandering Albatross
Diomedea exulans c. 20 nautical miles
off St. Helena Bay on 20 May,
with another on 25 May, a young
Grey-headed Albatross Thalassarche
chrysostoma on 15 May, with an adult
on 25 May, and single Spectacled
Petrels Procellaria ( aequinoctialis )
conspicillata on 10 April and 5 June.
In May, a Grey Petrel P. cinerea and
a Slender-billed Prion Pachyptila
belcheri were seen in southern African
waters from a vessel returning from
Marion Island. A pelagic trip c.50
km off Richards Bay, KwaZulu-
Natal, on 10-12 June produced a
Light-mantled Albatross Phoebetria
palpebrata, two Greater Frigatebirds
Fregata minor , 300+ Sooty Terns
Sterna fuscata and a Grey-headed
Kingfisher Halcyon leucocephala that
rested on the boat for a few hours
on 12th.
An immature Greater Frigatebird
stayed in the Durban area, KwaZulu-
Natal, from December 2009 until
at least late May. An Australian
Gannet Morus senator was seen on
Malgas Island, Western Cape, on
31 March and 31 May. Following
the influx of African Openbills
Anastomus lamelligerus throughout
the country in November-December
2009, birds were being seen during
the entire period. Most records
involved singles or small groups,
but in Western Cape a flock of 27
was at Elgin on 24 March (second-
largest for the province), whilst 1 1
were near Sedgefield on 9 June. In
Eastern Cape, 48 stayed at Mooiplaas
in March-April and 20 were present
at a small dam near the St. Francis
Links Golf Estate on 29 April. In
North West Province, 15 birds
stayed at Potchefstroom until at least
10 May, whilst in KwaZulu-Natal
at least 12 were near Ixopo on 31
May. Marabou Storks Leptoptilos
crumeniferus were seen in Western
Cape west of Heidelberg on 4 March
(one with a flock of White Storks
Ciconia ciconia ), at the N7 / M19
junction on 18 March (one), and at
Brandvlei Dam, near Worcester, in
late May (two).
An Osprey Pandion haliaetus in
Pilanesberg National Park, North
West, on 5 June was an unusual
record. Eurasian Honey Buzzards
Pernis apivorus were reported, in
Western Cape, near the top of
Kloof Nek Road on 27 February, at
Stellenbosch on 13 March, in the
Banghoek Valley near Stellenbosch
on 4 April and at Kenilworth on 3
May; in KwaZulu-Natal, one was
north of Durban on 3 April. A Bat
Hawk Machieramphus alcinus was
seen near Vogelfontein, Limpopo,
on 2-3 April, a Black-chested
Snake Eagle Circaetus pectoralis
near King Williamstown, Eastern
Cape, on 7 March and a Brown
Snake Eagle C. cinereus at the
Blaauwberg Hill Conservation Area,
Western Cape, in early March. A
Western Marsh Harrier Circus
aeruginosas was photographed at
Marievale Bird Sanctuary, Gauteng,
on 8 January, whilst a male Pallid
Harrier C. macrourus was observed
near Harrismith, Free State, in late
February. A Tawny Eagle Acjuila
rapax was present in the Imfolozi
Game Reserve, KwaZulu-Natal, on
30 May. A female Amur Falcon
Falco amurensis was seen near
Bredasdorp, Western Cape, on 27
February and a Sooty Falcon F.
concolor near the Afsaal Tea Room in
Kruger National Park, Mpumalanga,
on 9 April.
An African Crake Crex egregia
was found west of Port Elizabeth,
Eastern Cape, on 16 May and a
Spotted Crake Porzana porzana
at the Sappi Stanger wetlands,
KwaZulu-Natal, on 27 February.
In Limpopo, there were reports of
Striped Crake Aenigmatolimnas
marginalis from the Nylsvlei area
on 21 March and 2—3 April. Four
Black Crakes Amaurornis flavirostra
reported along the Orange River at
De Hoop, Northern Cape, on 21
April, were well out of range. In
Gauteng, a Wattled Crane Bugeranus
carunculatus was in a flock of 150+
Blue Cranes Anthropoides paradiseus
in farmland south of Devon on 1—23
May.
At least four Crab Plovers
Dromas ardeola stayed in the
Southern Sanctuary Area, Richards
Bay, KwaZulu-Natal, from August
2009 until at least mid May. A
Eurasian Oystercatcher Haematopus
ostralegus was at Bot River Lagoon,
Western Cape, from 1 1 March
until at least 24th. African Black
Oystercatchers H. moquini were
noted near Durban, KwaZulu-
Natal, on 29 May and 23 June. In
Western Cape, a Chestnut-banded
Plover Charadrius pallidus was seen
on the edge of Langvlei, Wilderness
National Park, on 12 June. A Lesser
Sand Plover C. mongolus was present
at Seeberg in West Coast National
Park, Western Cape, on 1 1—13
March, with at least two there on
14-25 March and a Broad-billed
Sandpiper Limicola falcinellus on
14 March and 3 April. At the same
250 - Bull ABC Vol 17 No 2 (2010)
Recent Reports
site, the sixth Hudsonian Godwit
Limosa haemastica for southern Africa
was found on 10 March and still
present on 25th. In KwaZulu-Natal,
Green Sandpipers Tringa ochropus
were reported in the period mid
December-mid February, including
one at Darvill Bird Sanctuary,
Pietermaritzburg, another at the
Sappi Stanger wetlands and a third
near Nyala Game Ranch.
A fishing trip in Western Cape
produced an adult Franklin’s Gull
Lams pipixcan a few miles off Sea
Point on 22 May; another was seen
feeding on emerging alates near the
Nxaxo estuary at Wavecrest, Eastern
Cape, on 10 June. An immature
Lesser Black-backed Gull L. fuscus
stayed at Orient Beach, East London,
Eastern Cape, throughout the period;
it was joined by an adult on 23
April. In Western Cape, a Roseate
Tern Sterna dougallii was located in
a roost of mostly Greater Crested
Terns S. bergii at Kommetjie on 10
March, whilst one in full breeding
plumage was found on Malgas
Island on 31 May. For the tenth
consecutive year, a Bridled Tern 5.
anaethetus returned to Cape Recife,
near Port Elizabeth, Eastern Cape,
in May; it was still there in late June.
In KwaZulu-Natal, south-east of
Mtunzini and c. 13 km offshore, a
Brown Noddy Anous stolidus landed
on a fishing boat on 2 April.
A Jacobin Cuckoo Clamator
jacobinus at Jakkelsfontein, south
of Yzerfontein, Western Cape, on
4 March, was an interesting record.
Also of interest was a Black Coucal
Centropus grillii on the western shore
of Lake St. Lucia, KwaZulu-Natal,
on 24 March. A European Nightjar
Caprimulgus europaeus was reported
near Rondevlei in Wilderness
National Park, Western Cape, on 18
May; this is an extremely uncommon
bird in the province. Two Swallow-
tailed Bee-eaters Merops hirundineus
were at Simon’s Town, on 2 June;
there are only a few previous records
from Western Cape. Two White-
fronted Bee-eaters M. bullockoides
stayed around the Tsitsikamma
Coastal Golf Estate, Eastern Cape, in
the early part of June. In Limpopo,
two White-throated Bee-eaters M.
albicollis in a group of European Bee-
eaters M. apiaster were photographed
at Balule Nature Reserve, on 18
March. In the Western Cape, four
Blue-cheeked Bee-eaters M. persicus
stayed near Sedgefield from late
February until early April. In the
same province, a Southern Yellow-
billed Hornbill Tockus leucomelas
reported from a farm c. 50 km north
ol Beaufort West, in May, appeared
to have been in the area for about a
year.
A male Yellow Wagtail Motacilla
flava was at Strandfontein Sewage
Works, Western Cape, on 11-18
March. In North West Province,
Tree Pipits Anthus trivialis stayed
at Kgaswane Nature Reserve near
Rustenburg from February; two
were still there on 2 March, with at
least one until 7 March. In Eastern
Cape, a vagrant Red-capped Robin
Chat Cossypha natalensis flew into a
window in St. Francis Bay on 2 May,
whilst one was caught by a cat in
Kimberley around the same time. A
Bush Blackcap Lioptilus nigricapillus
was reported from a Durban
garden on 13 June. A House Crow
Corvus splendens was noted in East
London, Eastern Cape, on 15 June.
A Red-billed Oxpecker Buphagus
erythrorhynchus was reported from
Keurbooms River Game Trails,
Western Cape, in May; local
rangers apparently have been seeing
oxpeckers there since February. The
area near Cofimvaba, in the former
Transkei, Eastern Cape, produced
a Black-chested Prinia Prinia
flavicans and a Scaly-feathered
Finch Sporopipes squamifrons in
early March; both species were well
south-east of their known ranges. In
Mpumalanga, a male Red-headed
Finch Amadina erythrocepbala was
reported from the Lower Sabie camp,
Kruger National Park, on 21 March
(per 777).
Tanzania
A Eurasian Wryneck Jynx torquilla
was photographed in Arusha
National Park on 1 1 January 2010;
this is apparently the first for the
country and it may well constitute
the southernmost record for this
species in Africa {ASK).
Togo
On 18 October 2009, at least 245
African Openbills Anastomus
lamelligerus flew south-west in small
groups along the Zio River north of
Lome. The same day, a mixed flock
of >800 terns was observed ar the
beach near Lome harbour. The flock
consisted of c.500 Common Terns
Sterna hirundo , r.200 Royal Terns S.
maxima and c. 100 Sandwich Terns
S. sandvicensis , with a few Black
Terns Chlidonias niger (JM & SM).
Tunisia
A visit in late October 2009 yielded
a flock of 1 1 Thick-billed Larks
Ramphocoris clotbey at Matmata on
21st and up to 30 Desert Sparrows
Passer simplex in Djebil National Park
on 21st-22nd, whilst a flock of 14
early Ring Ouzels Turdus torquatus
was observed on Djebel Chambi on
30th {HE).
Uganda
Records from November 2009-May
2010 include the following. An adult
Greater Spotted Eagle Aquila clanga
was photographed at Murchison Falls
National Park on 15 December (Fig.
21); although a few sight records
have been reported previously ( cf
Carswell et al. 2005. The Bird Atlas
of Uganda), the species does not
figure on the Uganda list, as no
substantiating details are available.
A juvenile Amur Falcon Falco
amurensis was observed at Ruhija,
Bwindi Impenetrable National Park,
on 3 December; there are few records
for the country ( DFo ).
Lesser Jacanas Microparra capensis
were seen at Mbwamba swamp on
10 January (three), Lake Opeta
on 26th (30+) and Lake Bisina
on 27th (three). A Little Ringed
Plover Charadrius dubius flew over
Muyenga on on 7 January; this is
an uncommon Palearctic visitor to
Uganda. Two Great Snipe Gallinago
media were at Nabugaba wetland on
7 March. A Caspian Tern Sterna
caspia was noted at Lutembe on
28 February (RS). A first-winter
Black Tern Chlidonias niger was
photographed among hundreds of
White-winged Terns C. leucopterus
on the Kazinga Channel, Queen
Recent Reports
Bull ABC Vol 17 No 2 (2010) -251
Figure 21. Greater Spotted Eagle /
Aigle criard Aquila clanga, Murchison
Falls National Park, Uganda, 15
December 2009 (Dick Forsman)
Figure 22. Black Tern / Guifette noire
Chlidonias niger, Kazinga Channel,
Queen Elizabeth National Park,
Uganda, 8 December 2009 (Dick
Forsman)
Elizabeth National Park, on 8
December (Fig. 22); this appears to
be the first for Uganda ( DFo ).
An African Skimmer Rynchops
flavirostris was at Makanaga swamp
on 2 May; this species is very local
in the country. A Black-throated
Barbet Tricholaema melanocephala
observed at the Katurum gate of
Kidepo Valley National Park, in the
north-east, on 17 January constitutes
the second record for Uganda, the
first dating from 1994. Palearctic
passerines seen during the same visit
and apparently not on the park’s list
include Tree Pipit Anthus trivialis
(fairly common), Eurasian Reed
Warbler Acrocephalus scirpaceus (two
singing) and Olivaceous Warbler
Hippolais pallida (one). Little Rush
Warblers Bradypterus baboecala
were seen and heard at Muyenga
swamp, Kampala, on 17 November
(one) and at a swamp between
Muyenga and Port Bell, on 1 January
(three). A pair of Southern Black
Flycatchers Melaenornis pammelaina
was observed at close range in Lake
Mburo National Park on 5-7 March;
the birds were glossy blue-black and
the song was very similar to a tape-
recording from Zambia, but unlike
that of Northern Black Flycatcher
M. edolioides. Although there have
been other recent records of Southern
Black Flycatchers from Mburo, the
species does not yet figure on the
Uganda list. An Isabelline Shrike
Lanius isabellinus was at Port Bell on
17 February. In January, six House
Sparrows Passer domesticus were seen
at the landing site at Bogota, and a
male was at Port Bell on 1 February.
Fox’s Weavers Ploceus spekeoides
were found at Lake Opeta (two) and
Lake Bisina (five) on 26-27 January.
A 'nuthatch weaver’ subsequently
identified as a female Yellow-capped
Weaver P. dorsomaculatus, was
observed in the Buhoma area of
Bwindi in December; this would
constitute another first for Uganda.
Also new for the country is Southern
Citril Serinus hypostictus, of which at
least ten were seen on the slopes of
Mount Elgon at Sipi on 5-7 April
(PS).
Zimbabwe
Reports from mid-December
2009-mid-February 2010 include a
Lesser Cuckoo Cuculus poliocephalus
in Vimba Forest and a Blackcap
Sylvia atricapilla in Mutarazi Falls
National Park, with another two near
Mutare. A Collared Palm Thrush
Cichladusa torquata that took up
residence in an Avondale garden in
Harare in April was well outside the
species’ known range (per 777).
Records were collated by Ron Demey
from contributions supplied by Jason
Anderson (JA), Nacho Aransay (NA),
Jean-Claude Beaudoin (JCB), Geert
Beckers (GB), Mark Beevers (MB),
Max Biasioli / Skua Nature (MBi),
Nik Borrow / Birdquest (1 SB), BirdLife
Botswana (BLB), Nicky Bousfield
(NBo), Chris Brewster ( CB), Joost
Brouwer (JB), Hugh Buck (HB),
Robert Burton (RB), Mohamed Balia
Conde (MBC), Robert J. Dowsett
(RJD), Frangoise Dowsett-Lemaire
(FD-L), Marchia Eifler (ME), Denis
Farges (DF), Ali Flatt (AF), Dick
Forsman (DFo), Alain Fosse (AFo),
Elmar Fuchs (EF), Matteo Gagliardone
/ Skua Nature (MG), Fraser Gear /
Rockjumper (FG), Trevor Hardaker
(TH), Jens Hering (JH), Harold
Hester (HH), David Hoddinott (DH),
Housseini Issaka (HI), Colin Jackson
( CJ), Adam Scott Kennedy (ASK),
David Kusserow (DK), Kevin Lambeets
(KL), Adam Manvell (AM), Johannes
Merz (JM), Sharon Merz (SM), Mark
Muller (MM), Liliana Pacheco (LP),
Wouter Plomp (WP), Bruno Portier
(BP), Remo Probst (RP), Andy Pugh
(AP), Thomas Rabeil (TR), Richard
Randall (RR), Nicola Scatassi / Skua
Nature (NS), Adrian Skerrett (AS),
Kadiatou Soumah (KS), Roger Skeen
(RS), Rainer Summers / Rockjumper
( RSu ), Botswana Tickbird (BT), Chris
Townend ( CT), Nicolas Vanermen
(NV), Cheryl Vroom ( CV), Tim
Wacher (TW), Stephen Walters (SW),
Ian White (IW), Inaki Zabala (IZ),
and from Africa — Birds & Birding,
Birding World, Dutch Birding,
capebirdnet, SARareBirdAlert,
www.zesforbirds.co.za and
sa-rarebirdnews@googlegroups.com.
Contributions for Recent Reports can
be sent to Ron Demey, Tenierslaan
24, B-3500 Hasselt, Belgium and
(preferably) by e-mail: rondemeyl @
gmail.com or recent_reports@
africanbirdclub. org
252 -Bull ABC Vol 17 No 2 (2010)
. Recent Reports
Reviews
Birding Ethiopia: A Guide to the
Country’s Birding Sites
Ken Behrens, Keith Barnes & Christian
Boix, 2010. Barcelona: Lynx Edicions. 189
pp, photographs and maps. Softback. ISBN
978-84-96553-55-2. UKE25.99.
Where to Watch Birds in
Ethiopia
Claire Spottiswoode, Merid Gabremichael
& Julian Francis, 2010. London, UK:
Christopher Helm. 192 pp, 266 photos and
29 maps. Softback. ISBN 978-1-4081-
3075-9. UKE19.99.
Bird books about Ethiopia have
been a bit like buses recently — we
have waited years for something and
suddenly several come along all at
once. Following hot on the heels of
the superb Field Guide to the Birds
of the Horn of Africa (see review in
Bull. ABC 16: 243—244), and the
equally excellent Birds of Ethiopia
and Eritrea: An Atlas of Distribution
(reviewed in Bull. ABC 17: 128-129)
comes not one but two guides on
bird-finding in Ethiopia.
These new books are very similar
to one another, which is perhaps to
be expected with site guides. Ethiopia
has a well-established history of
numerous bird tour operators and
independent birders visiting, and
both books draw heavily on the
accumulated knowledge from these
sources, as well as on information
supplied by the increasing number
of local guides. Indeed the Helm
book is co-authored by Merid
Gabremichael, one of the most
knowledgeable such guides in the
country.
Both works possess useful
introductory chapters describing
the country and discussing the
practicalities of travelling in Ethiopia,
a country both very different and
fascinating compared to the normal
experience of Western birders. There
is information on safety and security,
the best times to go, and suggested
itineraries. Both books serve the
purpose of a site guide admirably,
giving accurate directions to the
places they cover and descriptions of
what to look for at each site. There
are clear, easy to read maps in both
books, with GPS coordinates for
several sites, which really should
be a feature of all such site guides
these days. These are given within
the text in the Lynx book, but the
Spottiswoode et al. guide cross-refers
to an appendix containing all of the
GPS coordinates. The Helm guide
also advises that these are available
electronically from one of the authors
for uploading into your GPS,
which is a nice touch. Both books
are liberally peppered with superb
photos, some of birds that were until
recently of almost mythical status,
while the Helm guide has a useful
photographic guide to the 'top 30
birds’ towards the end.
Of the two, the Spottiswoode et
al. guide is the more comprehensive,
covering 30 different locations,
whereas Behrens et al. list just 26,
although some of these 26 include
sites that are treated separately in
the Helm volume. This greater
coverage allows the Helm book to
include such excellent birding sites as
Bahar Dar at the source of the Blue
WHERE TO WATCH BIROS IN
ETHIOPIA
Nile on the southern shores of Lake
Tana, and the ‘strange’ Gambella
in the south-west. Hopefully, this
greater coverage may tempt visiting
birders to explore a few places off
the beaten ‘endemic track’. The
brevity of the Lynx guide does have
its shortcomings. Bilen Lodge in
the Awash area is described in a few
lines as offering birding similar to
Awash National Park, which is really
not doing the site justice, while in
contrast the Helm book devotes
significantly more space to this
excellent region.
In terms of providing other
information useful for planning a
trip, I consider the Helm guide to
again be the superior of the two. The
list of contacts in the Lynx book is
woefully brief. Despite being told
earlier in the book that ‘several large
birding tour companies offer trips
to Ethiopia (see Contacts)’ there are
only two listed, both linked to the
tour company that the authors work
for. The Helm guide provides the
names of 21 contacts. Many of these
are hotels in key sites backed-up
with phone numbers. The list also
includes some of the best ground
agents — all really useful information
when planning a trip. These
comments aside, both books will
serve anyone visiting Ethiopia well
and, with the other books referred
Reviews
Bull ABC Vol 17 No 2 (2010) - 253
to in the opening paragraph, there
really is no excuse for not planning
a visit to this most interesting corner
of Africa. Indeed, hopefully, these
two site guides will encourage more
people to experience Ethiopia’s varied
wildlife — with a human population
rising almost exponentially, it needs
all the help it can get.
Steve Rooke
Complete Photographic Field
Guide: Birds of Southern Africa
Ian Sinclair & Peter Ryan, 2009. Cape
Town: Struik Nature. 432 pp, more than
2,500 colour photographs, 975 distribution
maps. Softback. ISBN 978-1-77007-388-3.
UKE24.99.
Vogel in Afrika. Ein fotografis-
cher Naturfiihrer fur Afrika
Rainer Christian Ertel, 2009. Nottuln: Fauna
Verlag. 398 pp, more than 1,300 colour pho-
tographs and distribution maps. Softback.
ISBN 978-3-935980-18-0. €49.00. (info@
fauna-verlag.de)
Although southern Africa is covered
by the widest range of ornithological
works on the African continent by
far, new bird books keep appearing.
The latest of these is a photographic
field guide by well-known birders
Ian Sinclair and Peter Ryan. Sinclair
already has a whole series of bird
guides to the region, including
photographic ones, to his credit,
so what’s new about this book?
The novelty principally resides in
the number and the quality of the
photographs. Indeed, the authors
can rightly claim to present the
most comprehensive collection of
photographs — more than 2,500
of them — of the region’s birds in
one handy volume. Instead of each
of the 975 species (including 17
from Antarctica and the Southern
Ocean) being illustrated by a single
photograph, as was the case in
previous guides, all now have at least
two, some even up to six. For only
four species no images were available;
these are illustrated by artwork. Per
plate, there are 2-7 species (usually
5-6), with 8-20 photographs (mostly
10-16). As some species, e.g. raptors,
COMPUTl PHOTOGRAPHIC HUD GUIDl
M’
of Southern Africa
4
Over 2 500 Image* A
lot accurate
" /
Sinclair
Peter Ryan
sasoL #4K
are illustrated with a relatively
large number of photographs on a
single plate, some images are only
thumbnails (see e.g. the harrier plate,
with 20 photos). However, as the
photographs are generally of high
quality, useful characteristics are
still visible. The species accounts,
on the opposite page, have been
substantially revised compared
to previous guides, and now also
provide weights and diet, and the
small but clear distribution maps
have been updated. A useful feature
is a calendar bar showing seasonality
of occurrence and breeding (an
improved version of the bar in the
Roberts Bird Guide , reviewed in Bull
ABC 15: 283-284, which shows
only breeding seasonality). The
book is attractively laid out, as we’ve
come to expect from this publisher,
and is a pleasure to browse. But
can it replace a ‘classic’ field guide
with colour paintings rather than
photographs? Despite the huge
improvements, the usual objections
against photographic guides remain
pertinent: not all plumages are
illustrated and, most importantly,
similar species are not conveniently
shown in similar postures. The
layout of the photographs, although
generally pleasing to the eye, also
does not allow the reader to quickly
grasp the clinching identification
features, as first one has to figure
out which images refer to each
species. On the positive side, it is
undoubtedly true that photographs
often better convey the ‘jizz’ of the
birds. As this well produced, rather
large (1 6.6 x 24.6 cm) book is
packed with information, much of
it not habitually included within a
‘classic’ field guide, it will usefully
complement such a guide.
How different is the German
book! Although it basically follows
the same, now standard, format of
plates opposite text and distribution
maps, we’re back to the photographic
guides of the 1 980— 90s, with a single
photograph for each species. This is
understandable, as the book presents
over 1 ,300 species from the whole
of Africa, with eight photographs
per page. Most images are good to
acceptable, but some are just ‘record
shots’, while others are not really
useful for identification purposes.
The accompanying species accounts,
which conveniently not only mention
German and scientific, but also
English names, are very brief, with
just 2—6 (generally 3—4) lines per
species, giving a succinct description
of identification features, habitat
and voice. Their brevity would not
necessarily be a drawback, if the
accompanying image clearly showed
each bird’s diagnostic features.
Unfortunately, this is not always the
case. Many pages have blank spaces
that could usefully have been filled
with essential additional information.
Although this book is presented as a
field guide, it is difficult to imagine
that a more or less serious birder
would be tempted to use it as such.
For the ‘bird-minded’ tourist, on
the other hand, this collection of
images may be insufficiently glossy
and attractive, and may confusingly
254 -Bull ABC Vol 17 No 2 (2010)
Reviews
contain too many species. So the
book appears to be some kind of
unsatisfying hybrid: neither a field
guide nor a coffee-table book.
This is a pity, especially as there
are extremely few recent books on
African birds in German.
Ron Demey
Sur les traces du roi des marais
(On the trail of the king of the
wetlands)
Genevieve Renson, 2008. Paris: Kubik
Editions. 159 pp, full colour throughout.
Hardback. ISBN-13: 978-2350830513.
UKE45.
This French-language book is an
unusual and beautifully produced
combination of wonderful photos
and descriptions of the wetland
environments where Shoebills
Bnlaeniceps rex occur, focusing on
two areas, including Bangweulu in
Zambia. The descriptions of the
local way of life and the often harsh
realities for the author in spending
33 months over a seven-year period
acquainting herself with the species,
occupy a very large proportion of
this large-format work. It is rather
more than a coffee-table book, which
after >100 pages describing the areas,
threats and other issues, goes on to
precis the species’ feeding, courtship
and breeding habits. For anyone with
an interest in natural history or in
visiting the wetland areas concerned,
this may well inspire interest in
the species and its biome — and the
book contains some engaging stories
of rescuing birds and the differing
perceptions of local people to the
author’s dedication to study the
species.
Considering the Shoebill’s near-
legendary status among naturalists,
it seems surprising that there has
not been a book or more scientific
papers dedicated to the species
before now, although the practical
difficulties make this gap rather more
understandable. The descriptions of
behaviour are certainly fascinating,
if somewhat anecdotal in style.
Whether systematic data were also
collected by the author and will be
published elsewhere is unclear, but it
seems unlikely. Very few publications
are cited, and I was left somewhat
concerned that more systematic
information quantifying the threats
may well be urgently needed.
But that is not what this book
sets out to do — it portrays the
extraordinary environment and
character of Shoebills, highlighting
the worrying declines, and I
strongly suspect it will successfully
generate interest and support for
conserving these seriously threatened
wetlands. The price is definitely
quite reasonable for such a high-
quality production, but to learn
about the species and its threats
as much or more information is
probably available on the BirdLife
International website or within Red
Data book accounts. The book has
received various awards and acclaim,
and for those interested in either the
habitat or this amazing species, it is a
book you will want to own!
Chris Bowden
Breeding Birds of the Western
Palearctic: Nests, Eggs,
Nestlings, Fledglings and
Habitats
Peter Castell & Richard Castell. Sheffield:
Birdguides Ltd. DVD covering 756 spp..
with 9,000 photographs. ISBN 978-1-
89811-050-7. Available from Birdguides.
com. UKE99.95.
As someone who has had a life-
long interest in the nesting habits
of African birds, I am awed by the
remarkable collection of 9,000
photographs of nests, eggs and
nestlings presented in this DVD.
Remarkable because there are nest,
egg and /or nestling photographs
for all but 20 of the 756 species that
breed in the Western Palearctic.
Nearly one-third of these species
also breed in Africa, so the DVD has
much of interest for African birders.
Finding and photographing a rare
bird can be challenging in itself,
but doing the same for the nest of
the same bird is another ball-game,
often requiring exceptional field skills
which the compilers of this DVD,
father and son, Peter & Richard
Castell, clearly have in abundance.
This, coupled with their exceptional
photographic ability, has resulted in
this most comprehensive pictorial
reference of how and where Western
Palearctic birds nest and what their
nests, eggs and nestlings look like.
The DVD is easy to use, with
an extensive introduction followed
by a species-by-species presentation
of breeding data and photographs.
One can access a species by using
the alphabetic listing or by following
family order. For each species
selected, small icons appear of the
nesting photographs, together with
a brief text outlining the bird’s
breeding habits, and clicking an
icon produces the enlarged image,
accompanied by a panel in which
the location and date where the
photograph was taken, is given,
plus the photographer’s name. The
vast majority of the images are by
Peter and Richard supplemented
by photographs from c. 100 other
photographers. For many commoner
birds there are 20-30 images per
species (Golden Eagle Aquila
chiysaetos top scores with 58 images),
Reviews
Bull ABC Vol 17 No 2 (2010) -255
while rarer species usually run to
fewer than ten.
In most species, the first images
are of the bird’s nesting habitat,
sometimes with the nest’s position in
a tree or shrub highlighted. Next is
a series of images of nests with eggs
or nestlings that, in the commoner
species at least, give coverage to the
variability that may exist in choice of
nest site or egg colour. Tawny Owl
Strix aluco nests, for example, are
shown in holes in trees, in buildings,
in nest boxes, in a crow Corvus nest,
and on the ground. The quality of
the photographs is mostly very good,
but it is clear that some of the older
photographs in the collection, from
the 1970s and 1980s, are inferior to
those taken more recently.
There is an understandable
reticence by most birders towards
investigating birds’ nests and nesting
behaviour given the bad publicity
that illegal egg collecting has
brought to the subject. This DVD
is published in association with the
British Trust for Ornithology (BTO)
and it is explained in much detail just
how many useful applications long-
term nest-monitoring programmes
have for conservation. Also that,
provided nest recorders adhere to the
BTO’s prescribed code of conduct
in this regard, nest recording can
be undertaken without impacting
negatively the breeding success of
the species involved. The success
of any nest-monitoring programme
is dependent on finding nests, and
finding nests is a skill that, given
the pace of today’s lifestyle, fewer
and fewer birders are inclined to
cultivate. As a result, among the most
challenging and rewarding aspects of
field ornithology are being passed by.
This DVD, with its superb collection
of images, will do much to kindle
such an interest and it provides an
invaluable reference for the Palearctic
species. Perhaps it will also lead to
a similar compilation for the sub-
Saharan avifauna.
Warwick Tarboton
Handbook of the Birds of the
World. Vol. 14 Bush-shrikes to
Old World Sparrows
Josep del Hoyo, Andrew Elliott & David
A. Christie (eds.), 2009. Barcelona: Lynx
Edicions. 893 pp, many colour plates and
photographs. Hardback. ISBN 978-84-
96553-50-7. UKE185.
With only two volumes to go,
following this one, how the editors
have managed to keep to such a
very tight production schedule is
nothing short of astonishing. This
volume (and the next one) will be
of particular interest to African
birders as it contains bushshrikes,
helmetshrikes, vangas, drongos,
crows, starlings and Old World
sparrows, although there are several
other families, mainly Australasian
endemics, including the bowerbirds
and birds-of-paradise. (Vol. 15
will include weavers, waxbills and
finches.)
The format must be well known
to just about everyone by now.
For each family a comprehensive
essay discusses taxonomy, ecology,
behaviour, conservation and
relationships with humans, all
accompanied by a series of usually
stunning photographs, many of
which involve birds engaged in
’interesting’ behaviour, i.e. they are
not merely portraits. This is followed
by the individual species accounts
accompanied by a series of excellent
plates (by several artists). These are
set out in a simple and clear format
under a series of main headings.
The taxonomy is commendably
up to date and treads a reasonable
course between ‘splitting’ and
‘lumping’. For example, it is noted
that Bulo Burti Bushshrike Laniarius
liberatus is now thought to be a
colour form within the Tropical
Boubou L. aethiopicus complex, but
L. erlangeri (containing ‘ liberatus )
and L. sublacteus are split, while L.
major is not. The series has, almost
inevitably, been ‘caught out’ by
some advances in taxonomy during
the course of its publication. For
example, several Malagasy endemics
whose affinities have been debated
for many years, such as the four
species of Newtonia and Ward’s
Flycatcher Pseudobias wardi, were
covered as warblers or flycatchers
in earlier volumes. These are now
usually considered vangas and would
therefore, as noted in the relevant
section, be better placed there.
As usual, the Foreword takes
the form of an essay on a topical
subject, this time the history and
development (past, present and
future) of birding by Stephen
Moss. It has a global perspective,
with sections on the early history,
developments through the 20th
century, the rise of citizen science
and the impact of amateurs on
scientific research and conservation,
as well as the economic benefits of
birding (which is being extensively
promoted in several parts of Africa).
Overall the series is superb.
Although quite costly to an
individual, there is usually a good
pre-publication offer. I doubt that
such a work will ever be repeated
in this form and if you need a
comprehensive review of the world’s
birds then there is no other choice.
Peter Lack
Also Received
Conservation: A Beginner’s
Guide
Paul Jepson & Richard Ladle, 2010. Oxford:
Oneworld Publications. 193 pp, several
black-and-white photographs. Softback.
ISBN 978-1-85168-714-5. UKE9.99.
A short introduction to many aspects
of conservation from two authors
who teach a M.Sc. course on the
subject.
256 -Bull ABC Vol 17 No 2 (2010)
Reviews
Letter to the Editor
On the birds of Omo Forest
Reserve, south-western
Nigeria
In their paper on the birds of Omo
Forest Reserve, south-west Nigeria,
Olmos & Turshak (2009) include a
photograph (their Fig. 4c) of a bird
which they identify as Pale-breasted
Illadopsis Illadopsis rufipennis. The
species is also mentioned briefly in
the accompanying text, as being one
that was readily detected by voice,
while in the annexed species list the
only illadopsises mentioned are I.
rufipennis and Brown Illadopsis /.
fulvescens, which are both shown as
being recorded by the authors and as
having previously been reported from
Omo by Green et al. (2007).
While not seeking to call into
question the occurrence of I.
rufipennis in Omo, there is reason
to believe that the bird in the
photograph is in fact Blackcap
Illadopsis /. cleaveri of the race
marchanti , which is confined to
southern Nigeria. This form differs
most obviously from all other
subspecies in having a grey, not
black, crown and is accordingly less
readily identifiable by sight, as well
as being less commonly illustrated.
The photograph, although taken
from below, shows part of the
hindcrown, where some evidence
of a contrasting cap can be seen,
appearing rather darker than the pale
grey ear-coverts. Moreover, the bird
has cinnamon breast-sides, flanks and
undertail-coverts, which are much
warmer-toned than the upperparts,
and pinkish-flesh legs. This
combination of characters points to I.
c. marchanti rather than /. rufipennis,
as the accompanying photographs
(Figs. 1-2) of skins in the Natural
History Museum (NHM), Tring,
make clear. The upper specimen
in both images is of I. c. marchanti
from Haro Forest Reserve, Ipake,
south-west Nigeria, while the lower
shows nominate I. rufipennis from
Awjawja, Lagos, also in south-west
Nigeria. The head pattern, leg colour
(even in these specimens) and, in
particular, coloration of the flanks, all
suggest that the bird in Fabio Olmos’
photograph is Blackcap Illadopsis,
not Pale-breasted.
This being the case, the record in
fact becomes more interesting as it
appears to be only the second time
that I. c. marchanti has been recorded
in south-west Nigeria. Indeed,
Ilaro Forest Reserve (06°53’N
03°01’E) is the only previously
known locality in this part of the
country (Elgood 1977), where /.
c. marchanti was trapped by Fry
(1964) and reported by Elgood et al.
(1994), as having been collected by
C. H. Fry, something to which the
accompanying photographs attest.
Oddly, I. cleaveri is not mentioned
from Ilaro by Button (1967), who
wrote only that Fry had mist-
netted I. rufipennis and /. fulvescens
(, moloneyanus ) there, whereas Fry
( 1 964) had listed I. rufipennis as
merely present but not captured, and
made no mention of I. fulvescens\
Some at least of this confusion may
have arisen from early uncertainty
as to the identity of Fry’s specimen,
for, as can be seen on one of the
labels, visible in the lateral view, the
original annotation reads ‘ Illadopsis
sp. indet.’, with 'cleaveri marchanti
evidently added later.
The paper by Olmos & Turshak
also includes records of two other
species which demand comment. The
first is that of Yellow-bellied Wattle-
eye Dyaphorophyia concreta. The
authors report ‘A pair with at least
one young foraging in the canopy...
the birds had vivid yellow underparts,
including the throat, typical of the
subspecies graueri' Two things
about these remarks raise concerns.
The first is that this species is a bird
of the understorey, not the canopy
(Erard 1997, Borrow & Demey
2001, Louette 2006; pers. obs.)
while, secondly, the throat, breast
and upper sides of the belly of female
D. concreta graueri are chestnut
(e.g. Erard 1997). Since Olmos &
Turshak imply that both birds of the
pair were all yellow this would appear
to eliminate D. concreta. Given also,
as the authors recognise, that their
record would represent the first of
this species away from south-eastern
Nigeria — the nearest known locality
is a specimen collected by Marchant
at Umuagwu, 05°20’N 06°53’E
(Marchant 1953) — we believe there
is sufficient doubt for it not to be
acceptable.
The other potentially contentious
record is that of Square-tailed
Drongo Dicrurus ludwigii. Olmos
& Turshak report three species of
drongo from Omo: Velvet-mantled
D. modestus , Shining D. atripennis
and Square-tailed. Of the last, they
state that ‘smaller drongos with
tails lacking obvious notches and a
purple-blue sheen were assigned to
this species’ noting that ‘singles and
pairs associated with mixed-species
flocks.
We believe that D. atripennis and
D. ludwigii have been much confused
in the past and indeed continue
to be; we are, however, unaware
of any confirmed co-occurrences
of these two species and consider
that all such published records to
the contrary require review. In our
experience, D. atripennis alone occurs
in primary and old secondary forest
at low to mid altitudes while, in
areas of broad sympatry, D. ludwigii
is confined to forest patches in
the forest-savanna transition zone,
rich gallery forest of the Sudanian
zone and areas of montane forest in
forest / grassland mosaics (e.g. on
the Obudu plateau, Nigeria: pers.
obs.). For example, records of D.
ludwigii from Makokou, Gabon, by
Letter to the Editor
Bull ABC Vol 17 No 2 (2010) -257
Figures 1-2. Specimens of Blackcap
Illadopsis Illadopsis cleaveri marchanti
(upper) and Pale-breasted Illadopsis
I. mfipennis rufipennis (lower) from
Nigeria (L. D. C. Fishpool © Natural
History Museum, Tring)
Specimens de l’Akalat a tete noire
Illadopsis cleaveri marchanti (en haut)
et de l’Akalat a poitrine blanche I.
rufipennis rufipennis (en bas) provenant
du Nigeria (L. D. C. Fishpool ©
Natural History Museum, Tring
Figure 3. Specimens of Square-tailed Drongo Dicrurus ludwigii (three left-hand birds) and Shining Drongo D. atripennis
(three right-hand birds) from Nigeria. The label data are explicit that two of the D. ludwigii specimens were collected from
‘a small wood in savanna [or orchard bush] country’ while all three D. atripennis were taken 'in the primary forest’ (L. D. C.
Fishpool © Natural History Museum, Tring)
Specimens du Drongo de Ludwig Dicrurus ludwigii (les trois oiseaux de gauche) et du Drongo de foret D. atripennis (les trois
oiseaux de droite) provenant du Nigeria. Le texte sur les etiquettes de recolte explique clairement que deux de ces D. ludwigii
proviennent d’une petite foret seche en savane boisee tandis que les trois specimens de D. atripennis ont ete obtenus dans la
foret primaire ombrophile (L. D. C. Fishpool © Natural History Museum, Tring)
Brosset & Erard (1986) have not
stood up to recent scrutiny. Repeated
subsequent visits to this locality
have revealed only D. atripennis (N.
Borrow in litt. to FD-L 2009) while
the recording ascribed to D. ludwigii
on Chappuis (2000) from north-east
Gabon is in fact of D. atripennis
(FDL; see also Dowsett-Lemaire &
Dowsett 1998: 7). Attention may
also be drawn to Bowden (2001)
who reports D. atripennis and D.
ludwigii as occurring together on
Mount Kupe, Cameroon. Our
experience of Kupe and of the forests
of neighbouring mountains indicates
only D. atripennis to be present
(Dowsett-Lemaire & Dowsett 1999;
pers. obs.).
We agree with Borrow & Demey
(2001) that detecting and assessing
the amount of gloss on the plumage
of D. atripennis in the gloom of the
forest interior can be very difficult.
Moreover, while the tail can appear
forked in some D. atripennis , in
others it may be little or no more
notched than it is in D. ludwigii.
These points are apparent in the
accompanying photograph (Fig. 3) of
Nigerian specimens of D. atripennis
(the three right-hand skins) and
D. ludwigii in NHM. This shows
that there is variation in the tail
shape of D. atripennis, from almost
un-notched (specimen third from
right) to shallowly forked (far right);
that the tail shape of D. atripennis
can approach that of D. ludwigii ( cfi. ,
e.g., D. atripennis second from right
with that of the D. ludwigii specimen
third from left) and that tail length
differences between the two species
are not always obvious. Although
the process of specimen preparation
may have had some effect here, these
comparisons are in line with our field
experience of the two species in the
region. Thus, tail notches measured
in D. atripennis mist-netted in south-
west Cameroon varied from 3 to
1 1 mm in depth; a seventh bird,
in moult, had a square tail because
258 -Bull ABC Vol 17 No 2 (2010)
Letter to the Editor
the outer feathers were still growing,
(RJD). In Lobeke (south -east
Cameroon) and northern Congo-
Brazzaville the tail of atripennis is
more deeply forked (FDL, RJD),
although this was not measured in
the one bird mist-netted.
Furthermore, the photograph also
illustrates the challenge in the field —
or, more precisely, the forest — of
discriminating the differences
between them in overall size,
particularly since they are not to be
seen together. Lastly, the differences
in the amount and intensity of gloss
can be seen to be minor, particularly
on the ventral surfaces; the contrast is
somewhat greater dorsally.
If we are correct in our view of
the ecological differences of these
two species, which result in their
mutual exclusion, a brief inspection
of the literature suggests that Olmos
& Turshak would not be alone
in confusing these two species. It
would also seem to indicate that a
full re-analysis of their respective
distributions across the range of D.
atripennis is required.
Acknowledgement
LDCF thanks Dr Robert Prys-Jones
of the Natural History Museum,
Tring, for access to skins.
References
Borrow, N. & Demey, R. 2001.
Birds of Western Africa. London,
UK: Christopher Helm.
Bowden, C. G. R. 2001. The birds
ol Mount Kupe, southwest
Cameroon. Malimbus 23: 1 3 — 44.
Brosset, A. & Erard, C. 1986. Les
Oiseaux des Regions forestieres du
Nord-est du Gabon. Vol. 1. Paris:
Societe Nationale de Protection de
la Nature.
Button, J. A. 1967. The birds of Haro
(II, part A). Bull. Niger. Orn. Soc.
4(15): 2-11.
Chappuis, C. 2000. African Bird
Sounds: Birds of North, West and
Central Africa and Neighbouring
Atlantic Islands. 1 5 CDs. Paris:
Societe d’Etudes Ornithologiques
de France & London, UK: British
Library.
Dowsett-Lemaire, F. & Dowsett, R.
J. 1998. Preliminary survey of the
fauna (in particular the avifauna)
of the reserves of Boumba-Bek
and Nki, south-eastern Cameroon.
Dowsett-Lemaire Misc. Rep.
no. 10, prepared for WWF-
Cameroon.
Dowsett-Lemaire, F. &: Dowsett,
R. J. 1999. Survey of birds and
amphibians on Mt Manenguba.
Mt Nlonako, north Bakossi
and around Kupe in 1998-99.
Unpubl. rep. to WWF-Cameroon.
Elgood, J. H. 1977. Forest birds
of southwest Nigeria. Ibis 119:
462-480.
Elgood, J. H., Heigham, J. B.,
Moore, A. M., Nason, A. M.,
Sharland, R. E. & Skinner, N.
J. 1994. The Birds of Nigeria: An
Annotated Check-list. BOU Check-
list No. 4. Second edn. Tring:
British Ornithologists’ Union.
Erard, C. 1997. Dyaphorophyia con-
creta. In Urban, E., Fry, C. H. &
Keith, S. (eds.) The Birds of Africa.
Vol. 5. London, UK: Academic
Press.
Fry, C. H. 1964. Shy or rare forest
birds at Ilaro: the value of mist-
netting. Bull. Niger. Orn. Soc.
1(1): 6-7.
Green, A. A., Hall, P. & Leventis, A.
P. 2007. Avifauna of Omo Forest
Reserve, SW Nigeria. Malimbus
29: 16-30.
Louette, M. 2006. Family
Platysteiridae (batises and wattle-
eyes). In del Hoyo, J., Elliott, A.
& Christie, D. A. (eds.) Handbook
of the Birds of the World. Vol. 11.
Barcelona: Lynx Edicions.
Marchant, S. 1953. Notes on the
birds of southeastern Nigeria. Ibis
95: 38-69.
Olmos, F. &t Turshak, L. G. 2009.
A survey of birds in Omo Forest
Reserve, south-western Nigeria.
Bull. ABC 16: 184-196.
L. D. C. Fishpool, BirdLife
International, Wellbrook Court, Girton
Road, Cambridge CB3 0NA, UK.
E-mail: lincoln.fishpool@birdlife. org
F. Dowsett-Lemaire & R. J. Dowsett,
Le Pouget, Sumene 30440, France.
E-mail: dowsett@aol.com
Letter to the Editor
Bull ABC Vol 17 No 2 (2010) - 259
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Notes for Contributors
The ABC welcomes original contributions on
all aspects of the birds of Africa, here defined
as the area covered by Collar, N.J. & Stuart,
S.N. 1985. Threatened Birds of Africa and
Related Islands: The ICBP/IUCN Red Data
Book. Cambridge, UK: International Council
for Bird Preservation, namely continental
Africa, Indian Ocean islands west of 80°E,
e.g. Madagascar, the Mascarene Islands and
Socotra; Atlantic Ocean islands on or east
of the mid-Atlantic ridge, e.g. the Tristan da
Cunha group, the Azores and the Canaries.
Contributions will be accepted subject
to editing and refereeing by independent
reviewers, where appropriate. The Editorial
Team will be happy to advise authors on
the acceptability of material at draft stage
if desired.
Submissions
Two hard (printed) copies should be sent
unless submitting by e-mail (preferred) to
the editor's address on the inside front cover.
Typewritten manuscripts should be double-
spaced, on one side of the paper only, with
wide margins all round. All submissions are
acknowledged.
Contributions are accepted in English
or French: French summaries are required
for all papers published in English, and vice
versa. Those submitting papers should supply
a summary for translation into English, or
French, as appropriate.
If you submit your contribution on CD
or floppy disk, please state computer (e.g.
IBM compatible PC, Macintosh) and word-
processing package (e.g. Word, WordPerfect)
used.
When sending your contribution on
disk, please do not key anything in ALL
CAPS (i.e. with the CAPS LOCK key
depressed) unless the combination always
occurs in that form (e.g. ‘USA’). Do not use
the carriage return key at the end of lines,
and do not right justify the margins. When
formatting tables use one tab, and not spaces,
between each column. Unless a sketch map
is provided as part of the article, the names
of places should follow those on standard or
readily available maps (preferably a recent
edition of The Times Atlas of the World).
Preferred names
Given the current instability over worldwide
lists of bird names, authors are requested to
follow those used in The Birds of Africa Vols.
1-7. The African Bird Club has recently pub-
lished (www.africanbirdclub.org/resources/
checklist.html) a checklist of birds in its
region. This is based on Birds of Africa but
incorporates more recent revisions where
appropriate. It includes preferred scientific,
English and French names, as well as races
and alternatives used by publications widely
used in Africa. For bird names this list should
be used or at least the preferred name used
there should be given as an alternative. For
non -Birds of Africa species (e.g. from the
Malagasy region) use Dowsett & Focbes-
Watson (1993). Deviation from such works
should be noted and the reasons given. The
Editorial Team will keep abreast of changes
in nomenclature and when an agreed list
of African names is available, will consider
switching to follow it.
Style
Authors are requested to follow conventions
used in the Bulletin of the African Bird Club
and to refer to a recent issue for guidance. A
detailed style guide can be obtained, either
electronically or as a hard copy, on request
from the Managing Editor.
Typesetting and layout by Alcedo Publishing, Arizona, USA • e-mail engli@egreenworks.us
Colour repro &t print production by Crowes of Norwich, UK • FSC accredited
• tel +44 (0)1603 403-349 • e-mail graphics@crowes.co.uk
Mixed Sources
Product group from well-managed
forests and other controlled sources
0 1996 Forest Stewardship Council
Ascension Island: John Hughes, The Old Shop, High
Street, Shipton Bellinger, Hampshire SP9 7UE, UK.
E-mail: rasuk@btconnect.com.
Angola: Pedro de Franca Doria vaz Pinto, Rua Helder
Neto 12, 7‘A; Luanda. E-mail: pvpinto@clix.pt.
Australia: K. David Bishop, PO Box 1234, Armidale,
NSW 2330. E-mail: kdbishop@ozemail.com.au.
Austria: Graham Tebb, Graf Starhemberggasse 20/14,
1040 Vienna. E-mail: tcbb@fwf.ac.at.
Belgium: Jan Goossens, Vruntebaan 18, 2520
Emblem. Tel/fax: +32 3 488 13 71. E-mail: jan.
goossens5@pandora.be.
Botswana: Chris Brewster, PO Box 26292, Gaborone.
E-mail: cbrewster@botsnet.bw.
Cameroon: DrTaku Awa II, Cameroon Biodiversity
Conservation Society (CBCS), PO Box 3055, Messa,
Yaounde. E-mail: takuawa@yahoo.co.uk.
Canada: Antonio Salvadori, 17 Colborn Street, Guelph,
Ontario. NIG 2M4. E-mail: Salvadori@rogers.com.
Canary Islands/Spain: Tony Clarke, Repriblica
Dominicana No. 61, Barrio de Fatima, 38500
Gtiimar, Tenerife. E-mail: bluechafifmch@
btopenworld.com.
Central African Republic: Nigel Voaden, 18 Fair Hill,
Shipham, Winscombe, Somerset BS25 1TH, UK.
E-mail: nigel.voaden@talk21.com.
Denmark: Uffe Gjol Sorensen, Ovengaden Oven
Vandet 68,2, 1415 Copenhagen. E-mail: ugs@post7.
tele.dk.
Democratic Republic of Congo: Byamana Robert
Kizungu, Head of Ornithology Laboratory, CRSN-
Lwiro, DRC. BP02 Cyangugu, Rwanda. E-mail:
kbyamana@yahoo.com.
Djibouti: Abdi Jama, c/o Guelle Osman Guelle,
PO Box 239, Djibouti City. E-mail: abdi.jama@
ymail.com.
Egypt: Sherif & Mindy Baha El Din, 2 Abdalla El
Katib St. Apt. 3, Dokki, Cairo. Tel/Fax: 3608160.
E-mail: egyptcalling@yahoo.com.
Eritrea: Russom Teklay, c/o Andeberhan Telday,
PFDJ, zone: Maekel, sub-zone: south east, PO Box
4618, Asmara. E-mail russotek79@yahoo.com.
Ethiopia: Mengistu Wondafrash, Ethiopian Wildlife
& Natural History Society, PO Box 13303, Addis
Ababa. E-mail: m.wondafrash@ewnhs.org.et.
France: Bob & Franchise Dowsett, Le Pouget,
Sumene, F30440. E-mail: Dowsett@aol.com.
Finland: Annika Forsten, Tornvalksv. 2 bst 15,
02620 Esbo. E-mail: annika.forsren@elisaner.fi.
Supported and Affiliated Membership
The Supporting Members scheme is a key part
of the Club’s strategy of encouraging the spread
of knowledge and understanding of birds as
widely as possible throughout Africa. The scheme
enables Africans who would not otherwise have
the resources to join, to become members of
the Club. The scheme is funded by Supporting
Members who pay a minimum of UKT30 to
cover their own membership and rhe subscription
of at least one African member. The money they
contribute over and above their own subscription
is placed in a special fund that is used ro cover
the membership expenses of African members
whom they may have nominated, or who have
been nominated by other Club members.
Although we have suggested a minimum
of UK£30 to become a Supporting Member,
any contribution is welcome. All members of rhe
Club, even if they do not feel able to become
Supporting Members themselves, are invited to
nominate candidates for supported memberships.
Candidates should be nationals of an African
country, with a genuine interest in wild birds
but without the resources to become members
in their own right. Africans who think they
may qualify are very welcome to put their own
ABC Representatives
The Gambia: Solomon Jallow, c/o WABSA,
Department of Parks & Wildlife, Management HQ,
Abuko Nature Reserve, Abuko, PMB 676 S/K.
E-mail: habitatafrica@hotmail.com.
Ghana: Samuel Kofi Nyame, PO Box KIA 30284,
Airport, Accra. E-mail: samknyame02@yahoo.com.
Italy: Giuseppe Micali, Via Volterra 3, Milano,
MI 1-20146. E-mail: xeaym@tin.it.
Kenya: George Were Eshiamwata, BirdLife
International, Africa Partnership Secretariat, ICIPE
Campus, Kasarani, PO Box 3502, 00100 GPO
Nairobi. E-mail: george.eshiamwata@birdlife.org.ke.
Liberia: Moses A. Massah, Society for the
Conservation of Nature of Liberia, Monrovia Zoo,
PO Box 2628, Monrovia. E-mail: mosesmassah@
yahoo.com.
Libya: Abdulmaula A. Hamza, Head, Marine
Conservation, Nature Conservation Dept.,
Environment General Authority EGA, Box 13793
Tripoli. E-mail: abdhamza@gmail.com.
Madagascar: J ulien Ramanampamonjy,
Section Oiseaux, PBZT, BP 4096, 101 Antananarivo.
E-mail: julien_asity@mel.moov.mg (mark FAO:
J ulien Ramanampamonjy).
Malawi: Tiwonge Mzumara, c/o Likhubula House,
PO Box 111, Mulanje. E-mail: tiwongem@yahoo.com.
Namibia: Tim Osborne, PO Box 22, Okaukuejo,
vis Outjo 9000. E-mail: kori@iway.na.
Nigeria: Phil Hall, A. P. Leventis Ornithological
Research Institute, Jos. E-mail: philhall.obe@
btinternet.com.
Rwanda: Marcell Claassen, Elegantafrica, PO Box 181,
Musanze. E-mail: marcell@elegantafrica.com
Sao Tome & Principe: Angus Gascoigne, CP 289,
Sao Tome. E-mail: agascoigne@eits.st.
Seychelles: Adrian Skerrett, Shipping House,
PO Box 336, Victoria, Mahe. Fax: 380538. E-mail:
malieship@seychelles.net or adrian@skerrett.fsnet.
co.uk.
Sierra Leone: Kenneth Gbengba, Conservation
Society of Sierra Leone, 2 Pyke Street, PO Box
1292, Freetown, Sierra Leone. E-mail: factsfinding@
yahoo.com.
Somaliland/Somalia: Abdi Jama, c/o Guelle Osman
Guelle, PO Box 239, Djibouti City, Republic of
Djibouti. E-mail: abdi.jama@ymail.com.
South Africa: Adam Riley, Managing Director,
Rockjumper Birding Tours, PO Box 13972, Cascades
3202. E-mail: info@rockjumper.co.za.
names forward, supporred by a letter of recom-
mendation from someone such as their employer,
teacher or an officeholder in a local wildlife
organisation.
The scheme now also includes clubs who
wish to be affiliated with the African Bird Club
in African countries where ir is difficult for local
individuals to become members in their own
right. Clubs accepted for membership under
the scheme receive up to six copies of each
issue of the bulletin for circulation among rheir
members. Instead of paying a membership fee,
Clubs are asked to provide a short annual report
on their activities that may be published in rhe
bulletin. Clubs interested in becoming Affiliated
Member Clubs are invited to apply to rhe ABC
Secretary giving details of their membership, their
constitution or a statement of their objectives
and conditions of their membership, and their
activities to date.
ABC Information Service
ABC offers a sendee to help members with
information requests. Perhaps you are planning
a trip to Africa and need local advice, or maybe
you are in search of an obscure fact about an
African species. The Club does not guarantee
Swaziland: Dr Ara Monadjem, UN1SWA, P/Bag 4,
Kwaluseni. E-mail: ara@tmiswacc.uniswa.sz.
Tanzania: Lota Melamari, CEO/Coordinator, Wildlife
Conservation Society of Tanzania, Garden Avenue,
Plot 39; PO Box 70919, Dar es Salaam. E-mail:
melamarilota@yahoo.co.uk.
Tunisia: Hichem Azafzaf, 1 1 rue Abou el alia el maari,
Cite el houda, 2080 Ariana. E-mail: azafzaf@gnet.tn.
Uganda: Prof. Derek Pomeroy, Makerere University
Institute of the Environment and Natural Resources,
PO Box 7298, Kampala. E-mail: derek@imul.com.
USA: Kurt Leuschner, 70065 Sonora Road #267,
Mountain Centre, CA 92561. E-mail: kleuschner@
collegeofthedesert.edu.
Zambia: Rod Tether, Kutandala Camp, North
Luangwa NP. E-mail: rod@kutandala.com
Zimbabwe: The Executive Officer, BirdLife
Zimbabwe, PO Box RVL100, Runiville, Harare.
E-mail: birds@zol.co.zw.
The ABC Representatives scheme aims to support
existing members by providing a local point of
contact in their region, for example, to answer queries
to the Club, to solicit submissions for the bulletin,
and possibly to arrange local meetings for members.
Existing ABC members can contact their local
Representative in the first instance with queries relating
to the Club. ABC Representatives help to recruit new
members in their region, for example, by distributing
posters and arranging local advertising. In Africa, ABC
Representatives help to identify opportunities to invest
the ABC Conservation Fund and candidates for the
Supported Membership scheme.
The Club aims to appoint many further ABC
Representatives. If you are interested in supporting
and promoting the Club in your region, have any
queries, or require further information relating to the
ABC Representatives scheme please do not hesitate to
contact the Membership Secretary at the Club address,
e-mail membership@africanbirdclub.org.
ABC is seeking Country Representatives in the
following countries, principally within the Club’s
region: Algeria, Azores, Benin, Burkina Faso, Burundi,
Cameroon, Cape Verde Islands, Chad, Comoros &
Mayotte, Cote d’Ivoire, Djibouti, Equatorial Guinea,
Gabon, Guinea-Bissau, Guinea Conakry', Madeira,
Mali, Mauritania, Mauritius, Morocco, Mozambique,
Netherlands, Niger, Reunion, Rodriguez, Senegal,
Socotra, Somalia, St Helena, Sudan, Togo, Tristan da
Cunha and USA.
to find all the answers but will try' to help. The
service is free to ABC members. Contact: Keith
Betton, who is also custodian of ABC’s journal
library', at 8 Dukes Close, Folly Hill, Farnham,
Surrey, GU9 ODR, UK. Tel: +44 1252 724068.
E-mail: info@africanbirdclub.org.
AfricanBirding e-mail discussion list
Launched, in October 2000, by the ABC and
the Pan-African Ornithological Congress,
AfricanBirding or AB, as it is known, has become
a useful forum for those interested in African
birds. To join the discussion, which averages
1-2 messages a day, send a blank e-mail to
AfricanBirding-subscribe@yahoogroups.com.
You will then receive an e-mail instructing you
how to join.
The Club also maintains a list of members’
e-mail addresses. This list is confidential and used
only for Club purposes, e.g. for informing mem-
bers of upcoming events and news concerning
the Club. It is not divulged to anybody outside
the Club or used for commercial advertising. At
present ir includes addresses for about 50% of
the membership. Please send any additions or
amendments to the membership secretary': mem-
bership@africanbirdclub.org.
Yellowbill / Malcoha a bee jaune Ceuthmochares aereus by Guy Upfold, www.birdinfo.co.za